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  <front>
    <journal-meta><journal-id journal-id-type="publisher">OS</journal-id><journal-title-group>
    <journal-title>Ocean Science</journal-title>
    <abbrev-journal-title abbrev-type="publisher">OS</abbrev-journal-title><abbrev-journal-title abbrev-type="nlm-ta">Ocean Sci.</abbrev-journal-title>
  </journal-title-group><issn pub-type="epub">1812-0792</issn><publisher>
    <publisher-name>Copernicus Publications</publisher-name>
    <publisher-loc>Göttingen, Germany</publisher-loc>
  </publisher></journal-meta>
    <article-meta>
      <article-id pub-id-type="doi">10.5194/os-18-797-2022</article-id><title-group><article-title>Coastal high-frequency radars in the Mediterranean – Part 2:
Applications in support of science priorities and societal needs</article-title><alt-title>Coastal HF radars in the Mediterranean</alt-title>
      </title-group><?xmltex \runningtitle{Coastal HF radars in the Mediterranean}?><?xmltex \runningauthor{E.~Reyes et al.}?>
      <contrib-group>
        <contrib contrib-type="author" corresp="yes" rid="aff1">
          <name><surname>Reyes</surname><given-names>Emma</given-names></name>
          <email>ereyes@socib.es</email>
        <ext-link>https://orcid.org/0000-0003-4350-739X</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Aguiar</surname><given-names>Eva</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-2411-1528</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2">
          <name><surname>Bendoni</surname><given-names>Michele</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Berta</surname><given-names>Maristella</given-names></name>
          
        <ext-link>https://orcid.org/0000-0001-5428-9741</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2 aff4">
          <name><surname>Brandini</surname><given-names>Carlo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff5">
          <name><surname>Cáceres-Euse</surname><given-names>Alejandro</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff6">
          <name><surname>Capodici</surname><given-names>Fulvio</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff7">
          <name><surname>Cardin</surname><given-names>Vanessa</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-4710-6844</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff8 aff9">
          <name><surname>Cianelli</surname><given-names>Daniela</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff6">
          <name><surname>Ciraolo</surname><given-names>Giuseppe</given-names></name>
          
        <ext-link>https://orcid.org/0000-0001-6627-0175</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Corgnati</surname><given-names>Lorenzo</given-names></name>
          
        <ext-link>https://orcid.org/0000-0001-5819-7713</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff10">
          <name><surname>Dadić</surname><given-names>Vlado</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2 aff4">
          <name><surname>Doronzo</surname><given-names>Bartolomeo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff11">
          <name><surname>Drago</surname><given-names>Aldo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff5">
          <name><surname>Dumas</surname><given-names>Dylan</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff9 aff12">
          <name><surname>Falco</surname><given-names>Pierpaolo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2 aff4">
          <name><surname>Fattorini</surname><given-names>Maria</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-5801-7302</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff13">
          <name><surname>Fernandes</surname><given-names>Maria J.</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff11">
          <name><surname>Gauci</surname><given-names>Adam</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff14">
          <name><surname>Gómez</surname><given-names>Roberto</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Griffa</surname><given-names>Annalisa</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff5">
          <name><surname>Guérin</surname><given-names>Charles-Antoine</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff15">
          <name><surname>Hernández-Carrasco</surname><given-names>Ismael</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-4574-0198</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Hernández-Lasheras</surname><given-names>Jaime</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-5986-4001</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff16 aff17">
          <name><surname>Ličer</surname><given-names>Matjaž</given-names></name>
          
        <ext-link>https://orcid.org/0000-0003-2304-2505</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff18 aff19">
          <name><surname>Lorente</surname><given-names>Pablo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Magaldi</surname><given-names>Marcello G.</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-0742-9673</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Mantovani</surname><given-names>Carlo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff10">
          <name><surname>Mihanović</surname><given-names>Hrvoje</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff5">
          <name><surname>Molcard</surname><given-names>Anne</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Mourre</surname><given-names>Baptiste</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Révelard</surname><given-names>Adèle</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff7">
          <name><surname>Reyes-Suárez</surname><given-names>Catalina</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-3906-471X</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff8 aff9">
          <name><surname>Saviano</surname><given-names>Simona</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Sciascia</surname><given-names>Roberta</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2">
          <name><surname>Taddei</surname><given-names>Stefano</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff15">
          <name><surname>Tintoré</surname><given-names>Joaquín</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff20">
          <name><surname>Toledo</surname><given-names>Yaron</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff8 aff9">
          <name><surname>Uttieri</surname><given-names>Marco</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff10 aff21">
          <name><surname>Vilibić</surname><given-names>Ivica</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-0753-5775</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff9 aff22">
          <name><surname>Zambianchi</surname><given-names>Enrico</given-names></name>
          
        <ext-link>https://orcid.org/0000-0001-5474-7466</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff15">
          <name><surname>Orfila</surname><given-names>Alejandro</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-1016-8726</ext-link></contrib>
        <aff id="aff1"><label>1</label><institution>SOCIB, Balearic Islands Coastal Observing and Forecasting System, Palma, 07122, Spain</institution>
        </aff>
        <aff id="aff2"><label>2</label><institution>Consorzio LaMMA, Sesto Fiorentino, 50019, Italy</institution>
        </aff>
        <aff id="aff3"><label>3</label><institution>Consiglio Nazionale delle Ricerche (CNR), Istituto di Scienze
Marine (ISMAR), Lerici, 19032, Italy</institution>
        </aff>
        <aff id="aff4"><label>4</label><institution>Consiglio Nazionale delle Ricerche (CNR), Istituto per la
Bioeconomia (IBE), Sesto Fiorentino, 50019, Italy</institution>
        </aff>
        <aff id="aff5"><label>5</label><institution>Mediterranean Institute of Oceanography, Université de
Toulon, Aix Marseille Univ., <?xmltex \hack{\break}?>CNRS, IRD, MIO, Toulon,  France</institution>
        </aff>
        <aff id="aff6"><label>6</label><institution>Università degli Studi di Palermo, Dipartimento di Ingegneria, 90128, Palermo, Italy</institution>
        </aff>
        <aff id="aff7"><label>7</label><institution>Instituto Nazionale di Oceanografia e di Geofisica Sperimentale
(OGS), Sgonico, 34010, Italy</institution>
        </aff>
        <aff id="aff8"><label>8</label><institution>Stazione Zoologica Anton Dohrn, Naples, 80121, Italy</institution>
        </aff>
        <aff id="aff9"><label>9</label><institution>Consorzio Nazionale Interuniversitario per le Scienze del Mare
(CoNISMa), Rome, 00196, Italy</institution>
        </aff>
        <aff id="aff10"><label>10</label><institution>Institute of Oceanography and Fisheries, Split, 21000, Croatia</institution>
        </aff>
        <aff id="aff11"><label>11</label><institution>Physical Oceanography Research Group, University of Malta, Msida,
MSD 2080, Malta</institution>
        </aff>
        <aff id="aff12"><label>12</label><institution>Universita' Politecnica delle Marche, DISVA, Ancona, 60121, Italy</institution>
        </aff>
        <aff id="aff13"><label>13</label><institution>Qualitas Instruments Lda., Caparica, 2825-182, Portugal</institution>
        </aff>
        <aff id="aff14"><label>14</label><institution>Helzel Messtechnik GmbH, 24568 Kaltenkirchen,  Germany</institution>
        </aff>
        <aff id="aff15"><label>15</label><institution>Mediterranean Institute for Advanced Studies – IMEDEA-
(CSIC-UIB), Esporles, 07190, Spain</institution>
        </aff>
        <aff id="aff16"><label>16</label><institution>National Institute of Biology, Marine Biology Station, Piran,
6330, Slovenia</institution>
        </aff>
        <aff id="aff17"><label>17</label><institution>Slovenian Environment Agency, Ljubljana, 1000, Slovenia</institution>
        </aff>
        <aff id="aff18"><label>18</label><institution>NOLOGIN CONSULTING SL, Zaragoza, 50018, Spain</institution>
        </aff>
        <aff id="aff19"><label>19</label><institution>Puertos del Estado, Área de Medio Físico, Madrid, 28042, Spain</institution>
        </aff>
        <aff id="aff20"><label>20</label><institution>School of Mechanical Engineering, Tel-Aviv University, Tel-Aviv,
6905904, Israel</institution>
        </aff>
        <aff id="aff21"><label>21</label><institution>Ruđer Bošković Institute, Division for Marine and
Environmental Research, Zagreb, 10000, Croatia</institution>
        </aff>
        <aff id="aff22"><label>22</label><institution>Dipartimento di Scienze e Tecnologie (DiST), Parthenope University
of Naples, Naples, 80133, Italy</institution>
        </aff>
      </contrib-group>
      <author-notes><corresp id="corr1">Emma Reyes (ereyes@socib.es)</corresp></author-notes><pub-date><day>1</day><month>June</month><year>2022</year></pub-date>
      
      <volume>18</volume>
      <issue>3</issue>
      <fpage>797</fpage><lpage>837</lpage>
      <history>
        <date date-type="received"><day>30</day><month>November</month><year>2021</year></date>
           <date date-type="rev-request"><day>14</day><month>December</month><year>2021</year></date>
           <date date-type="rev-recd"><day>5</day><month>April</month><year>2022</year></date>
           <date date-type="accepted"><day>13</day><month>April</month><year>2022</year></date>
      </history>
      <permissions>
        <copyright-statement>Copyright: © 2022 Emma Reyes et al.</copyright-statement>
        <copyright-year>2022</copyright-year>
      <license license-type="open-access"><license-p>This work is licensed under the Creative Commons Attribution 4.0 International License. To view a copy of this licence, visit <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">https://creativecommons.org/licenses/by/4.0/</ext-link></license-p></license></permissions><self-uri xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022.html">This article is available from https://os.copernicus.org/articles/18/797/2022/os-18-797-2022.html</self-uri><self-uri xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022.pdf">The full text article is available as a PDF file from https://os.copernicus.org/articles/18/797/2022/os-18-797-2022.pdf</self-uri>
      <abstract><title>Abstract</title>

      <p id="d1e607">The Mediterranean Sea is a prominent climate-change hot
spot, with many socioeconomically vital coastal areas being the most
vulnerable targets for maritime safety, diverse met-ocean hazards and marine
pollution. Providing an unprecedented spatial and temporal resolution at
wide coastal areas, high-frequency radars (HFRs) have been steadily gaining
recognition as an effective land-based remote sensing technology for
continuous monitoring of the surface circulation, increasingly waves and
occasionally winds. HFR measurements have boosted the thorough scientific
knowledge of coastal processes, also fostering a broad range of
applications, which has promoted their integration in coastal ocean
observing systems worldwide, with more than half of the European sites
located in the Mediterranean coastal areas. In this work, we present a
review of existing HFR data multidisciplinary science-based applications in
the Mediterranean Sea, primarily focused on meeting end-user and
science-driven requirements, addressing regional challenges in three main
topics: (i) maritime safety, (ii) extreme hazards and (iii) environmental
transport process. Additionally, the HFR observing and monitoring regional
capabilities in the Mediterranean coastal areas required to underpin the
underlying science and the further development of applications are also
analyzed. The outcome of this assessment has allowed us to provide a set of
recommendations for future improvement prospects to maximize the
contribution to extending  science-based HFR products into societally
relevant downstream services to support blue growth in the Mediterranean
coastal areas, helping to meet the UN's Decade of Ocean Science for
Sustainable Development and the EU's Green Deal goals.</p>
  </abstract>
    </article-meta>
  </front>
<body>
      

<sec id="Ch1.S1" sec-type="intro">
  <label>1</label><title>Coastal monitoring to support blue growth in the Mediterranean Sea</title>
      <p id="d1e619">The coastal and ocean economy has been since ancient times and is now,
more than ever, the backbone of the Mediterranean countries' blue economy.
In 2017, the Mediterranean was the third largest sea basin in terms of gross
value added (GVA) and the first in terms of employment (European Commission,
2020). The key sector is clearly coastal tourism, from which the
Mediterranean is the world's leading destination, followed by maritime
transport, living resources and port activities. Furthermore, coastal
tourism and fisheries benefit from the location of the marine protected
areas (MPAs), which currently cover 7 % of the northern
Mediterranean Sea surface (Meola et al., 2019) and are expected to increase
as one of the goals of the United Nations (UN) Decade of Ocean Science for
Sustainable Development.</p>
      <p id="d1e622">Mediterranean coastal areas and communities are, however, negatively
impacted by all human activities related to these traditional sectors.
Regarding the sector of maritime transport, it is worth highlighting that
the Mediterranean Sea is one of the world's busiest shipping lanes of oil
and gas tankers, container vessels, and ships, involving a higher risk of
marine oil and marine litter (ML) pollution. Although the extent of the
latter is not fully understood yet, first estimations provided from
Cózar et al. (2015) identify the Mediterranean Sea as a great
accumulation zone of plastic debris comparable to the accumulation
zones described for the five subtropical ocean gyres. Additionally,
Soto-Navarro et al. (2021) have recently found that the hot spots for the
ML risk concentrate in the coastal regions, highly impacting
Mediterranean biodiversity, especially in the MPAs and particularly in
those near ML sources.</p>
      <p id="d1e625">Given the strategic role of ports in the globalized trading system, it is
important to underline that four ports from the Mediterranean (i.e.,
Algeciras, Valencia, Piraeus and Marseille) are included in the top-five
European ports when looking at different categories according to the
Eurostat statistics from 2020. Moreover, the Mediterranean Sea hosts the
three main migratory routes to Europe, representing a huge humanitarian,
political and security challenge for the bordering countries. In this
context, we cannot ignore the more than 99 400 migrants who arrived in Europe
in 2020, mainly by sea and particularly to Spain, Greece and Italy by
crossing the Mediterranean Sea according to the data from the International
Organization for Migration (IOM). This complex migratory hub contributes to
the increased risk to life and maritime safety in the Mediterranean.</p>
      <p id="d1e628">Last but not least, as recently reviewed by Tintoré et al. (2019), the
Mediterranean is one of the most vulnerable regions in the world due to the
impact of climate change. As a result of large-scale warming, among many
other impacts reported by the authors, an increase in frequency and/or
intensity of extreme events is expected (Mitchell et al., 2006). In this
context, De Alfonso et al. (2021) points out an average of eight storms per
year registered for the Spanish Mediterranean coast with particular severe
events registered in November 2001 (Gómez et al., 2002), October 2007
(Cohuet et al., 2011), December 2008 (Sánchez-Arcilla et al., 2014),
January 2017 and January 2020 (Amores et al., 2020; de Alfonso et al., 2021,
Lorente et al., 2021; Sotillo et al., 2021). Aiming to monitor and
understand this regional and sub-regional ocean state and variability from
daily to interannual scales, a set of indicators for the Mediterranean Sea
and the Balearic Islands (Juza and Tintoré, 2021) are made available
through a user-friendly visualization tool by SOCIB (Tintoré et al.,
2013, 2019).</p>
      <p id="d1e632">The increased capability to address the abovementioned regional challenges
at the required spatiotemporal scales has directly benefited, inter alia, from the
key features of high-frequency radar (HFR hereinafter) technology, i.e.,
unprecedentedly high spatiotemporal resolution (i.e., 0.2–6 km and 15–60 min)
over wide coastal areas (up to 200 km offshore, depending on the operational
frequency). HFRs provide continuous monitoring of the surface circulation
(Lipa, Barrick and Maresca, 1981; Paduan and Graber, 1997; Headrick and
Thomason, 1998; Molcard et al., 2009; Paduan and Washburn, 2013; Wyatt,
2014; Roarty et al., 2019; Dumas and Guérin, 2020), increasingly, wave
parameters (Lipa et al., 1990, 2005, 2006; Gurgel et al., 2006; Wyatt et
al., 2006; Orasi et al., 2018; Wyatt and Green, 2009; Long et al., 2011;
Wyatt, 2011; Falco et al., 2016; Saviano et al., 2019, 2020, 2022; Basáñez
et al., 2020; Bué et al., 2020) and, occasionally, wind field (Long and
Trizna, 1972; Heron, 2002; Huang et al., 2004; Shen et al., 2012; Kirincich
et al., 2016a; Zeng et al., 2016, 2018; Shen and Gurgel, 2018; Saviano et
al., 2021). This land-based remote sensing technology gives us a unique
insight to coastal ocean state and variability with relative ease in terms
of technical effort, manpower and costs (i.e., for the same amount of
information and compared to other conventional observing platforms),
allowing us to improve our understanding of sub-mesoscale and mesoscale
coastal processes.</p>
      <p id="d1e635">Moreover, coastal ocean surface current and wave real-time information,
which represents the primary and secondary basic products of HFRs,
respectively, is being used extensively by search and rescue (Ullman et
al., 2006; Ličer et al., 2020; Révelard et al., 2021), environmental
agencies for pollutant monitoring of oil spills (Abascal et al., 2009),
marine litter tracking (Declerck et al., 2019), recreational activities,
navigational safety, ports and shipping, ship detection and tracking
(Ponsford et al., 2001; Dzvonkovskaya et al., 2007; Maresca et al., 2013;
Laws et al., 2016), coastal and offshore engineering applications,
aquaculture, marine renewables (Wyatt, 2012; Basáñez and
Pérez-Muñunzuri, 2021; Mundaca-Moraga et al., 2021), and early
warning detection systems for natural hazards (Lipa et al., 2006; Gurgel et
al., 2011; Grilli et al., 2015; Guérin et al., 2018), among others.
Furthermore, the mapping of surface currents at high spatiotemporal
resolution provided by the HFRs in the coastal strip allow us to use them as
a ground truth for coastal model real-time assessment (Wilkin and Hunter,
2013; Lorente et al., 2016, 2019b; Mourre et al., 2018; Aguiar et al., 2020)
and improvement through HFR data assimilation (Breivik and Saetra, 2001;
Paduan and Shulman, 2004; Barth et al., 2008; Iermano et al., 2016;
Hernández-Lasheras et al., 2021), as well as for the evaluation of
coastal remote sensing products (Manso-Narvarte et al., 2018; Caballero et
al., 2020; Gommenginger et al., 2021). The development of advanced HFR data
products such as gap-filled nowcasts and Lagrangian trajectories allows us to
satisfactorily estimate transport, making HFR data a key asset in the
assessment and protection of the coastal marine environment, including
dispersal and retention of particles (Cianelli et al., 2017;
Hernández-Carrasco et al., 2018a; Davila et al., 2021), cross-shelf
exchanges and transport (Sciascia et al., 2018), eddy tracking (Nencioli et
al., 2010; Bagaglini et al., 2020), and 3D eddy characterization
(Manso-Narvarte et al., 2021).</p>
      <p id="d1e638">In addition to this, many strong coordinated efforts to significantly
increase the prompt distribution, availability, easy access and accuracy of
HFR data have been made in recent years at the global (Roarty et al., 2019),
European (Rubio et al., 2017) and regional levels (Lorente et al., 2022),
also leveraged by national initiatives and specific projects. These joint
efforts have enhanced the creation of a community at the HFR operator level,
therefore accelerating the speed of the take-up of data, also
underpinning the growth of HFR multidisciplinary applications worldwide
(Fujii et al., 2013; Paduan and Washburn, 2013; Wyatt, 2014; Rubio et al., 2017 and Roarty et al., 2019).</p>
      <p id="d1e641">This broad range of applications has also boosted the positive trend in HFR installation all around the world. Consistently, HFRs are also
currently playing a crucial role as one of the backbones of the coastal ocean
observing systems – COOSs – of the Mediterranean Sea, which currently
encompass more than half of the existing HFR systems installed in
Europe (Lorente et al., 2022), therefore constituting an important focus of
HFR activity.</p>
      <p id="d1e644">Demonstrating the potential of the HFR observing and monitoring regional
capabilities, this work reviews the existing mature and emerging scientific
and societal applications using HFR data, developed to address the major
challenges identified in the Mediterranean coastal waters, organized around
three main topics: (i) maritime safety, (ii) extreme hazards and (iii) environmental transport processes. Also recognizing the added value of
networking, it is worth highlighting that this review encompasses the main
outcomes of multidisciplinary, international and intersectoral regional
coordinated efforts in the framework of the Mediterranean Operational Network
for the Global Ocean Observing System (MONGOOS) HFR Task Team. These
endeavors are primarily focused on meeting end-user and science-driven
requirements, aiming to unlock HFR data potential and deliver greater
uptake, use and value from the data for the benefit of ecosystems,
services and human activities of the coastal areas of the Mediterranean Sea.</p>
      <p id="d1e647">This paper constitutes the second part of two complementary
contributions, the first one providing a detailed overview of the main
achievements, ongoing activities, future challenges and the roadmap towards
an integrated, mature HFR network in the Mediterranean Sea (Lorente et al.,
2022). The sections of this paper are as follows: Sect. 2 presents several
HFR applications addressing science priorities and societal needs,
classified in the abovementioned three topics. Section 3 includes the
discussion and a preliminary assessment of the capabilities of the existing
HFR applications. Based on this assessment, Sect. 4 outlines the future
prospects for HFR applications along with a set of key recommendations
aiming to leverage the HFR data to their fullest extent, thus helping to
harness HFR potential in the further development of operational
monitoring systems at the regional level.</p>
      <p id="d1e651">This contribution will help to achieve the goals of the United Nations
(UN) Decade of Ocean Science for Sustainable Development (Ryabinin et al.,
2019) and to address the transitional changes required towards the European
Green Deal (Sikora, 2021). Finally, a summary and the main conclusions are
provided in Sect. 5.</p>
</sec>
<sec id="Ch1.S2">
  <label>2</label><title>High-frequency radar applications in the Mediterranean</title>
      <p id="d1e662">This section presents the existing advanced and emerging scientific and
societal applications using HFR data, aiming to address science priorities
and societal needs identified in the Mediterranean coastal waters (Lorente
et al., 2022), organized around three main topics: (i) maritime safety,
(ii) extreme hazards and (iii) environmental transport processes.</p>
<sec id="Ch1.S2.SS1">
  <label>2.1</label><title>Maritime safety</title>
      <p id="d1e672">Around 200 000 large vessels operate annually in the Mediterranean Sea,
including ferries as well as cargo and commercial vessels, among which around 300 tankers
transport oil-based products every day, accounting for more than 350 million
tons per year (more than 25 % of the world's oil tonnage) as highlighted
by Di Muccio et al. (2020). This intense maritime traffic makes the basin a
susceptible area in terms of oil spills, search and rescue (SAR) operations,
and other maritime emergencies. Over the past half-century spills over the
sea from tankers have shown a downward trend, reaching the lowest number in early
2020 due to the global health and economic crisis triggered by the COVID-19
pandemic (March et al., 2021). However, oil spills as well as chemical
spills and other hazardous substance releases are still present, putting
marine health at risk. For instance, in the second half of February 2021,
around 170 km of coastline from Israel to southern Lebanon suffered from a
large oil spill (García-Sánchez et al., 2022), one of the worst
ecological disasters in decades. In this context, accurate forecasting of
oil spill modeling (for this particular event, the model MEDSLIK-II was
used, as described in De Dominicis et al., 2013a, b) and Lagrangian
trajectory analysis of floating objects (Sayol et al., 2014; Ličer et
al., 2020) have been demonstrated to successfully help marine SAR operations and
oil spill containment. These forecasts depend strongly on the accuracy of
the forcing data (i.e., wind, waves and currents, as stated in Sect. 2.1.2)
ingested in atmospheric and oceanographic models, for which ocean
surface current maps from HFRs in particular can greatly improve short-term model outputs
due their high resolution and their near-real-time nature (Abascal et al., 2009, 2012; Breivik et al., 2013), as described in Sect. 2.1.3. In this context real-time HFR data were accepted as a reliable
operational tool for SAR, oil spill and other operational protocols in
coastal waters (Roarty et al., 2019). Concerning the last two sections, it
is important to mention the wider implementation of  ocean models and
short-term predictions in other crosscutting areas from the three addressed
main topics. Nevertheless, we have included them in this section to
highlight the HFR strengths for SAR applications through model assessment
and improvement, backtracking, and short-term forecasting.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F1" specific-use="star"><?xmltex \currentcnt{1}?><?xmltex \def\figurename{Figure}?><label>Figure 1</label><caption><p id="d1e677">Map of the Mediterranean showing the HFR mean spatial coverage
(pink contours) and the location of SAR incidents of France, Italy, Slovenia
and Spain from 2019 colored based on their distance to the closest coastal
point. For further details about the operational status and the names of the
HFR systems the reader is referred to Lorente et al. (2022). In order to
indicate the detail of the coverage of the HFRs and their proximity to the incident
locations in particular areas, Figs. S1, S2 and S3, available in
the Supplement, show zoomed-in views of Italy, the northwestern
Mediterranean sub-basin and the Strait of Gibraltar, respectively.</p></caption>
          <?xmltex \igopts{width=398.338583pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f01.png"/>

        </fig>

<sec id="Ch1.S2.SS1.SSS1">
  <label>2.1.1</label><title>Search and rescue</title>
      <p id="d1e693">Agencies in charge of SAR operations, marine pollution response and maritime
traffic control are among the most significantly targeted users of reliable
met-ocean information. Access to multi-platform quality-controlled near-real-time met-ocean observations and high-resolution forecasts available for
their specific areas of responsibility for marine SAR, assigned by the IMO
(International Maritime Organization), is essential for them to support
emergency response missions. Wind, wave and surface current observations
and forecasts are needed to be seamlessly integrated into their SAR
emergency tools in order to predict the trajectory of a drifting target for
determining the optimal search region. In the sphere of maritime safety,
HFRs have the great advantage of providing high-spatiotemporal-resolution
surface currents in wide coastal areas very close to the coastline when HFR
gap-filling methods are applied (listed in Sect. 2.1.3) and where most of
the SAR incidents occur (as shown by Fig. 1), as the review of the
location of the SAR incidents from five countries (i.e., Croatia, France, Italy,
Slovenia and Spain) along 2019 and from Malta along 2020 clearly shows.
<list list-type="custom"><list-item><label>i.</label>
      <p id="d1e698"><italic>Croatia</italic>. A total of 612 SAR interventions were registered in 2019, 389 of which are
SAR interventions and 223 are MEDEVAC ones (i.e., actions related to
transportation of injured or sick persons). Most of these incidents occur
during summer from June to September and over 98 % in inner and
territorial waters. Coastal waters from Croatia are operationally monitored
by the HFR-SPLIT WERA Radar System, consisting of two WERA HFR sites
(Ražanj and Stončica) in the eastern part of the eastern
mid-Adriatic basin. The HFR-NASCUM system is a historical network located in
the eastern part of the Gulf of Venice. All four sites were used to build
NEURAL project short-term predictions (described in Sect. 2.1.3).</p></list-item><list-item><label>ii.</label>
      <p id="d1e704"><italic>France</italic>. France has five SAR responsibility areas in the continental littoral
coordinated by 340 SAR operators from the five maritime rescue coordination
centers, including one for the French Mediterranean responsibility area. In
2019, a total of 13 507 SAR incidents occurred (with 22 313 people assisted),
51 % of which were from June to September, as indicated on the website of
the French Ministry of the Sea. In particular, the number of SAR incidents
in the French Mediterranean responsibility area accounts for 23 % (3110)
of the total number of cases and 32 % (7293) of the people assisted, as
included in the 2019 activity report of the French Mediterranean
Coordination Center. A total of 94 % of SAR incidents occur in coastal areas in
the first 12 nm (22.2 km) and mostly during summer season (from June to
September), with more of the 89 % related to recreational boating and
sailing. Currently, two HFR networks are operating in the French
Mediterranean coastal waters of Nice and Toulon, named HFR-MedTln and
HFR-MedNce.</p></list-item><list-item><label>iii.</label>
      <p id="d1e710"><italic>Italy</italic>. SAR operations are under the responsibility of the Italian
coast guard covering 500 000 km<inline-formula><mml:math id="M1" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> of sea and 8000 km of coast. In 2019
the Italian coast guard responded to 1875 SAR missions, 226 of them related
to human migration. SkyTruth, a non-governmental agency, reported one spill
60 km south of Genoa in the Ligurian Sea. Six HFR networks are currently
monitoring the coastal areas of the Tyrrhenian and Ligurian Sea (HFR-TirLig)
as well as the Tuscan Archipelago (HFR-LaMMA), Gulf of Naples (HFR-GoN), the
Malta–Sicily Channel (HFR-CALYPSO), and the northern Adriatic Sea and the Gulf
of Trieste (HFR-NAdr), with one recently deployed in the southwest of Sicily
island (HFR-SIC). Two additional HFR networks in the Gulf of Manfredonia
(HFR-GoM) and the Gulf of Venice (HFR-NASCUM) are historical deployments.</p></list-item><list-item><label>iv.</label>
      <p id="d1e725"><italic>Malta</italic>. There is one maritime rescue coordination center with around 50
SAR operators, covering one search and rescue region (SRR) of 267 874 km<inline-formula><mml:math id="M2" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> with 196.8 km of coastline (including Comino and Gozo). During 2020,
429 missions were coordinated by the MRCC (Maritime Rescue Coordination
Centre) in Malta, 26 % of which were reported as SAR cases occurring
within Maltese territorial seas. The HFR-CALYPSO monitors the Malta–Sicily
Channel, accounting for seven HFR sites and the HFR-CALYPSO-SOUTH, and is composed
of two HFR sites located in the south of Malta. HFR data are combined with
forecast model outputs to get the best representation of the sea state
during SAR operations.</p></list-item><list-item><label>v.</label>
      <p id="d1e740"><italic>Slovenia</italic>. Slovenia has 42 km of coastline and a semi-enclosed coastal area.
During 2019, the SAR agency responded to nine SAR missions (seven times the
rescue boat went out to sea, while two rescues were of injured people on a
moored boat in port). All cases occurred within 3 nm from the coast
(i.e., three within 200 m, three around 1 nm and one at 3 nm from the coast). The
HFR-NAdr, in the northern Adriatic Sea and the Gulf of Trieste, is jointly
operated through transnational collaboration with Italy.</p></list-item><list-item><label>vi.</label>
      <p id="d1e746"><italic>Spain</italic>. The four SAR responsibility areas cover 1 500 000 km<inline-formula><mml:math id="M3" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> of marine
surface (3 times the size of the Spanish national territory) and 8000 km of
coastline. The Spanish Maritime Safety and Rescue Agency (SASEMAR
hereinafter) is divided into 19 MRCCs plus one national center, with more than
370 SAR operators. SASEMAR responded to 5891 missions in 2019, almost 88 % of which
were SAR operations. A total of 50 % of the total SAR incidents
occurred within 3 km of the Spanish coastlines. Of the seven HFR networks
operating inside their four responsibility areas, three of them are located in the
western Mediterranean, monitoring the Strait of Gibraltar (HFR-Gibraltar),
the Ebro Delta (HFR-Ebro) and the Ibiza Channel (HFR-Ibiza), and all of them
are integrated in the SASEMAR Environmental Data Server.</p></list-item></list>
As previously mentioned, maritime SAR operations most often depend on leveraging
Lagrangian tracking tools using timely and reliable knowledge of surface
circulation, near-surface winds and, if applicable, surface gravity waves.
Surface circulation is generally provided by numerical circulation models,
but HFR observations can offer valuable insight into marine conditions over
the region of the accident and can – especially when coupled to short-term
prediction models (see Sect. 2.1.3) – act as a complementary input for
Lagrangian predictions, hindcasts or backtracking simulations. Révelard
et al. (2021) evaluated the use of HFR-derived trajectories to complement
drifter observations for assessing the performance of different models (i.e.,
GLO-MFC, IBI-MFC and MED-MFC, provided by the Copernicus Marine Service and WMOP)
in predicting Lagrangian trajectories. They used the skill score (SS)
metric based on the normalized cumulative Lagrangian separation distance
(Liu and Weisberg, 2011), which is a commonly used metric for assessing
Lagrangian performance. They have concluded that, whereas drifters only
provide assessment along their drifting paths, HFR allows for a large number
of trajectories, improving not only the robustness of the skill score
statistics but also the spatial and temporal assessment of the model
performance (Fig. 2). Since HFR data are quasi-continuous in time, this
method can be applied in near-real time, which is a strong advantage for
evaluating extremely scenario-dependent models. Indeed, the quality of any
numerical model performance varies with time and can have substantial
fluctuations on short temporal and spatial scales even if the model
otherwise exhibits good overall forecasting skills. In cases like these,
quality-controlled HFR observations represent particularly valuable
short-term inputs for Lagrangian products assisting SAR efforts.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F2" specific-use="star"><?xmltex \currentcnt{2}?><?xmltex \def\figurename{Figure}?><label>Figure 2</label><caption><p id="d1e763">Temporally averaged skill score SS<inline-formula><mml:math id="M4" display="inline"><mml:msup><mml:mi/><mml:mo>∗</mml:mo></mml:msup></mml:math></inline-formula> obtained for four models as
indicated in the title of each panel by comparing against the HFR-derived
trajectories of the Ibiza Channel during a forecast time of 6 h.
Simulated trajectories are initialized hourly at each grid point on
30 September 2014 from 13:00 to 16:00 <bold>(a–d)</bold>, on 28 July 2016 from 16:00
to 22:00 <bold>(e–h)</bold>, and on 15 November 2018 from 13:00 to 16:00 <bold>(i–l)</bold>. SS<inline-formula><mml:math id="M5" display="inline"><mml:msup><mml:mi/><mml:mo>∗</mml:mo></mml:msup></mml:math></inline-formula> values, with red representing the higher average model
performance, are only obtained in those grid points with data temporal
availability equal to or higher than 80 %. Black lines show the drifter paths
available during the same periods, and the boxes indicate the regions where
the averages are applied for comparison with the results obtained with
drifter observations. Original source: from Révelard et al. (2021).</p></caption>
            <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f02.png"/>

          </fig>

      <p id="d1e799">Aiming to improve the applicability of this model assessment methodology for
SAR operations in coastal areas, Révelard et al. (2021) also analyzed
the SS sensitivity to different forecast horizons and showed that in
coastal regions (i) the SS is sensitive to the forecast time, i.e., the
longer the forecast (i.e., 72 h), the higher the SS value, due to the
high variability of the surface currents; and (ii) a shorter forecast time (e.g.,
6 h), consistent with the duration of the search that maximizes
survivors in SAR missions, is therefore more appropriate. In addition, they
have shown that, whereas the original definition of the skill score from Liu
and Weisberg (2011) is correct for analyzing its spatiotemporal
distribution, the use of a novel skill score (SS<inline-formula><mml:math id="M6" display="inline"><mml:msup><mml:mi/><mml:mo>∗</mml:mo></mml:msup></mml:math></inline-formula>) is recommended to assess
the average model performance over an area of interest and along a specified
period to avoid biased conclusions. The advantage of the SS<inline-formula><mml:math id="M7" display="inline"><mml:msup><mml:mi/><mml:mo>∗</mml:mo></mml:msup></mml:math></inline-formula> is that,
despite its similar formulation to the SS defined by Liu and Weisberg
(2011), SS<inline-formula><mml:math id="M8" display="inline"><mml:msup><mml:mi/><mml:mo>∗</mml:mo></mml:msup></mml:math></inline-formula> does not impose negative values to zero, allowing us to obtain
a correct average, as in Fig. 2. However, they clarified that only SS<inline-formula><mml:math id="M9" display="inline"><mml:msup><mml:mi/><mml:mo>∗</mml:mo></mml:msup></mml:math></inline-formula>
values <inline-formula><mml:math id="M10" display="inline"><mml:mrow><mml:mo>&gt;</mml:mo><mml:mn mathvariant="normal">0.5</mml:mn></mml:mrow></mml:math></inline-formula> should be interpreted as  good agreement between
HFR surface current observations and model outputs.</p>
      <p id="d1e849">A further academic study of the value of quality-controlled HFR observations
in SAR operations was the recent case of a person lost at sea in the
northern Adriatic during a Sirocco storm on 29 October 2018. In this case,
HFR-NAdr observations were employed for hindcasting and survivor's drift
trajectory verification (Ličer et al., 2020). Figure 3 depicts Lagrangian
drifter dispersal computed from modeled surface winds (the dominant
contribution to the drift in this case) and HFR surface currents from the
HFR-NAdr network in the Gulf of Trieste after this accident.</p>
      <p id="d1e852">Even though in this case part of the survivor's trajectory outside  the
HFR-NAdr domain had to be inferred from extrapolated currents, such
HFR-based nowcasting products would have been valuable during this and
similar rescue attempts. However, since HFR data arrive in near-real time,
some sort of model-based extension of their prediction horizon is necessary
before they can be used for operational nowcasting. One possible solution is
data assimilation of HFR data into a numerical model (see Sect. 2.1.2.),
followed by a forecasting time window. An alternative and numerically less
demanding option that has gained ground in recent years is the machine-learning
approach whereby a neural network model is trained on past data and then used
to create short-term predictions of surface currents, as addressed in Sect. 2.1.3.</p>
</sec>
<sec id="Ch1.S2.SS1.SSS2">
  <label>2.1.2</label><title>Model assessment and improvement</title>
      <p id="d1e864">This section addresses one of the main interests and needs of end users of
operational oceanography information: users want to be able to have
confidence in modeled data and they need to know how good they are.
Addressing end-user overarching concerns, model assessment, essentially
built upon comparison to observations, is crucial to evaluate the quality of
the diversity of modeling products available in a systematic and long-term
routine manner and to inform users about their usefulness for a given
application.</p>
      <p id="d1e867">For this reason, also seeking to strengthen end-user loyalty, the validation
of operational ocean forecasting systems against independent measurements
constitutes a core activity in operational oceanography (Hernández et
al., 2015) since it aids in (i) inferring the relative strengths and weaknesses
in the modeling of several key physical processes, (ii) comparing
different versions of the same operational ocean forecasting system and
evaluating potential improvements and degradations before a new version is
transitioned into operational status, (iii) comparing coarse-resolution
“parent” and nested high-resolution “child” systems to quantify the
added value of downscaling, and (iv) informing end users about the consistency
and skill of the modeling products disseminated.</p>
      <p id="d1e870">Developments in ocean modeling have clearly advanced to address the
challenges associated with the increased resolution and its application to
coastal areas, also responding to the high demand for providing 4D estimates
of multiple oceanic variables at fine scales (Mourre et al., 2018;
Fox-Kemper et al., 2019). Coastal modeling faces numerous challenges and
issues such as downscaling and representation of open boundary conditions or
land–sea and air–sea interactions (Kourafalou et al.et al., 2015a). Synergies
between models and ocean observations are needed to face these challenges
and improve representation of ocean processes (Kourafalou et al., 2015b; De
Mey-Frémaux et al., 2019; Davidson et al., 2019). Additionally, it is
worth mentioning the current lack of real-time and historical availability
of observations in coastal areas, which limits the operational
capability and reduces the potential of skill assessment operational
services aiming to provide synthetic metrics addressing specific user
needs (Révelard et al., 2021).</p>
      <p id="d1e873">Within this context, HFR systems play a first-order role thanks to their
unique ability to provide fine-resolution maps of the surface currents over
broad coastal areas. This ability of HFR systems makes them particularly
appropriate for the validation of numerical models in coastal areas, where
other observations are scarce and/or their resolutions (i.e., in space or in
time) are not high enough to capture the fine scale. Many HFR systems have
therefore been used for this purpose in several regions of the
Mediterranean Sea including the Northern Current area off Toulon (Berta et
al., 2014a), the Ebro Delta area (Lorente et al., 2016, 2021; Ruiz et al., 2020;
Aguiar et al., 2020;  Sotillo et al., 2021), the
northern Adriatic (Vilibić et al., 2016), the Gulf of Naples (Uttieri et
al., 2011), the Ibiza Channel (Mourre et al., 2018; Aguiar et al., 2020;
Révelard et al., 2021; Sotillo et al., 2021) and the Strait of Gibraltar
(Lorente et al., 2019a; Aguiar et al., 2020).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F3" specific-use="star"><?xmltex \currentcnt{3}?><?xmltex \def\figurename{Figure}?><label>Figure 3</label><caption><p id="d1e879">Using HFR currents for Lagrangian hindcasting of an accident on 29 October 2018 in the Gulf of Trieste; details in Ličer et al. (2020). Blue
arrows denote the HFR surface current field on 29 October 2018 at 22:00 UTC. Thinner
(but scaled to length) light blue arrows depict nearest-neighbor
extrapolated currents outside the HFR domain (every third point is plotted
for clarity). Red dots denote modeled virtual drifter locations after 24 h of the drift, starting from the accident location (white circle at
13.495<inline-formula><mml:math id="M11" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> E, 45.4635<inline-formula><mml:math id="M12" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> N). The green line indicates the survivor's estimate of his
drift trajectory. Adapted from Ličer et al. (2020).</p></caption>
            <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f03.png"/>

          </fig>

      <p id="d1e906">An example of this added value of  HFR data was recently shown in the
multi-model comparison exercise performed in the Strait of Gibraltar in 2017
(Lorente et al., 2019a). In that case, the IBI-MFC model (Sotillo et al.,
2015) was compared against their partially nested SAMPA (Sánchez-Garrido
et al., 2013) high-resolution coastal forecast system to elucidate the
accuracy of each system characterizing the Atlantic Jet (AJ) inflow
dynamics. To this aim, HFR-derived hourly currents at the midpoint of the
selected transect (square in Fig. 4a) were used as a benchmark. The
scatter plot of HFR-derived hourly current speed versus direction (taking as
a reference the north and positive angles clockwise) revealed interesting
details (Fig. 4b): (i) the AJ flowed predominantly eastwards, forming an
angle of 78<inline-formula><mml:math id="M13" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> with respect to the north; (ii) the current
velocity, on average, was 1 ms<inline-formula><mml:math id="M14" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> and reached peaks of 2.5 ms<inline-formula><mml:math id="M15" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>.
Speeds below 0.5 ms<inline-formula><mml:math id="M16" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> were registered along the entire range of
directions; (iii) westward currents, albeit in the minority, were also
observed and tended to predominantly form an angle of 270<inline-formula><mml:math id="M17" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>
(i.e., towards the Atlantic), mostly related to intense easterly winds
episodes (Garret, 1983; García-Lafuente et al., 2002; Menemenlis et
al., 2007; Péliz et al., 2009; Reyes et al., 2015; Lorente et al., 2019a, b; Bolado-Penagos et al., 2021), as further detailed in Sect. 2.2.1.
The scatter plot of SAMPA estimations presented a significant resemblance in
terms of prevailing current velocity and direction (Fig. 4c). Although the
time-averaged speed and angle were slightly smaller (0.9 ms<inline-formula><mml:math id="M18" display="inline"><mml:mrow><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup><mml:mo>)</mml:mo></mml:mrow></mml:math></inline-formula> and
greater (88<inline-formula><mml:math id="M19" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>), respectively, the main features of the AJ
were qualitatively reproduced: maximum velocities (up to 2.5 ms<inline-formula><mml:math id="M20" display="inline"><mml:mrow><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup><mml:mo>)</mml:mo></mml:mrow></mml:math></inline-formula> were
associated with an eastward flow and an AJ orientation in the range of
50–80<inline-formula><mml:math id="M21" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>. Surface flow reversals
to the west were also properly captured. By contrast, noticeable differences
emerged in the scatter plot of regional IBI-MFC estimations (Fig. 4d):
surface current velocities below 0.3 ms<inline-formula><mml:math id="M22" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> were barely replicated, and
the AJ inversion was only observed very occasionally. Despite the fact that
IBI-MFC appeared to properly portray the mean characteristics of the
eastward flow, the model tended to favor flow directions between
60 and 180<inline-formula><mml:math id="M23" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> and to overestimate the current
velocity, with averaged and maximum speeds around 1.17 and 2.80 ms<inline-formula><mml:math id="M24" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>,
respectively.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F4" specific-use="star"><?xmltex \currentcnt{4}?><?xmltex \def\figurename{Figure}?><label>Figure 4</label><caption><p id="d1e1048"><bold>(a)</bold> HFR-derived mean surface circulation pattern in the Strait of
Gibraltar for 2016–2017: classical Atlantic Jet inflow into the
Mediterranean, with strong surface currents flowing to the NE. Solid black
squares represent radar sites. The black line and the related white square
indicate the selected transect and its midpoint, respectively. <bold>(b–d)</bold> Quantitative validation at the selected grid point (5.43<inline-formula><mml:math id="M25" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> W,
35.99<inline-formula><mml:math id="M26" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> N) within the Strait of Gibraltar: annual (2017)
scatter plot of hourly current speed versus direction (angle measured
clockwise from the north); estimations provided by HFR-Gibraltar <bold>(b)</bold>, SAMPA
high-resolution coastal model <bold>(c)</bold> and IBI-MFC <bold>(d)</bold>, a regional model into which
SAMPA is nested. Mean and standard deviation values of both AJ speed
and direction are gathered in black boxes. Magnitudes of the complex
correlation (i.e., CC index) and phase between HFR and model-predicted
currents are provided in red font. Adapted from Lorente et al. (2019a).</p></caption>
            <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f04.png"/>

          </fig>

      <p id="d1e1090">In summary, HFR measurements are able to precisely assess the added value of
the downscaling performed through the SAMPA coastal system with respect to
the IBI-MFC regional solution in which SAMPA is nested. Overall, a steady
improvement in the Atlantic Jet characterization is evidenced in model
performance when zooming from regional to coastal configurations,
highlighting the benefits of the downscaling approach adopted and also the
potential relevance of a variety of factors at local scale, among others: a
more refined horizontal resolution, a tailored bathymetry or the higher
spatiotemporal resolution of the atmospheric forcing. Furthermore, SAMPA
appeared to better reproduce the reversal events detected with HFR
estimations, demonstrating the added value of imposing accurate
meteorologically driven barotropic velocities in the open boundaries,
imported from the NIVMAR storm surge model (Álvarez-Fanjul et al.,
2001), in order to consider the remote effect of the atmospheric forcing
over the entire Mediterranean basin, which was only partially included in
IBI-MFC.</p>
      <p id="d1e1093">During the next phase of the Copernicus Marine Service, more focus
will be on coastal downstream applications (e.g., very high-resolution ocean
models integrated with coastal observatories) for a wide range of coastal
stakeholders including ports and environmental agencies. Despite the
significant progress in the field of coastal modeling, some storm-induced
hazards are still not properly resolved (or even misrepresented) by ocean
models due to a variety of factors (e.g., horizontal resolution that is too coarse,
inadequate meteorological forcing, poor representation of land–sea
interactions and the related river freshwater outflows, among others) as
described by Sotillo et al. (2021). Within this framework, HFR might act as
a monitoring cornerstone to calibrate and validate successive, upgraded
versions of operational ocean forecasting models with the aim of better
capturing extreme events in terms of strength, extension and timing (Lorente
et al., 2021).</p>
      <p id="d1e1097">Aguiar et al. (2020) used the three HFR systems available in the western
Mediterranean Sea (Strait of Gibraltar, Ibiza Channel – described in Tintoré
et al., 2013, and Lana et al., 2016 – and Ebro Delta) to evaluate the impact
of downscaling on the surface coastal circulation in the case of the Western
Mediterranean OPerational forecasting system (WMOP) (Juza et al., 2016;
Mourre et al., 2018). The authors showed that the time-average circulation
in the coastal areas of the Ebro Delta and Ibiza Channel were improved
through downscaling. In particular, the nested model showed a better
representation of the small-scale coastal flow intensification at the mouth
of the Ebro River and a refinement in the characterization of the
circulation in the Ibiza Channel. Notice that HFR-Gibraltar, HFR-Ebro and
HFR-Ibiza versus model comparisons are updated daily on the SOCIB WMOP web page
<uri>https://socib.es/?seccion=modelling&amp;facility=wmedvalidation</uri>
(last access: 9 May 2022).
Those HFR systems,
among others, are also integrated in the IBISAR science-based data
downstream service (Reyes et al., 2020a) – freely available under
registration at <uri>https://www.ibisar.es/</uri> (last access: 9 May 2022) – for visualizing, comparing and
evaluating the performance of ocean current predictions in the
Iberian–Biscay–Irish regional seas. IBISAR allows the identification of the
most accurate ocean current dataset in a specific area and period of
interest, thus facilitating decision-making for SAR operators and emergency
responders. Lorente et al. (2022) consider the IBISAR service to be a
successful example of the long-lasting engagement built in collaboration
between HFR operators and end users (i.e., the Spanish Maritime Safety and
Rescue Agency). Additionally, those HFR systems are also being used for
IBI-MFC model assessment purposes by means of the NARVAL multiparameter and
multi-platform validation tool (Lorente et al., 2019c) for IBI-MFC model
validation.</p>
      <p id="d1e1106">Another added value of HFR systems is their use to improve model forecast
through data assimilation (DA). DA aims at optimally combining observations
and models to provide a better representation of the ocean dynamics. In this
sense, HFR provides very valuable high-resolution observations in areas
where satellite observations tend to suffer from limitations due to the vicinity
of the coast (Vignudelli et al., 2019). While the assimilation of HFR
measurements has been applied in many regions of the world since the first
studies from Breivik (2001) and Oke et al. (2002), only a limited number of
studies have been performed in the Mediterranean Sea. Marmain et al. (2014)
assimilated radial velocity observations from the Toulon HFR system in a
regional model in the Gulf of Lion. They showed how HFR observations can be
successfully used to correct the wind forcing used to constrain the model
coastal surface circulation. In the Ligurian Sea, Vandenbulcke et al. (2017)
were able to correct surface currents and improve the representation of
inertial oscillations after the assimilation of all the available hourly
radial observations in a regional model of the area. Variational methods
were also applied to improve model dynamics through multi-platform data
assimilation including HFR in the southern Tyrrhenian Sea (Iermano et al.,
2016) and in the Adriatic Sea (Janeković et al., 2020).</p>
      <p id="d1e1109">More recently, Hernández-Lasheras et al. (2021) specifically assessed
the impact of assimilating HFR observations on the surface currents in the
Ibiza Channel using the WMOP operational system. They compared the
performance of both radial and total daily mean HFR-Ibiza surface currents
(Tintoré et al., 2013, 2020) for correcting mesoscale and sub-mesoscale
circulation using different initialization methods in an operational-like
context. An independent Lagrangian validation performed by comparing
non-assimilated and assimilated (without and with HFR) measurements with a set of
14 surface drifters (Tintoré et al., 2014) showed that the best results
were obtained when using HFR total observations along with the traditional
observation sources (i.e., satellite altimetry, sea surface temperature –SST,
and Argo temperature and salinity profiles). After 48 h, the mean
separation distance between virtual buoys and real drifters was reduced by
53 % compared to the simulation without any data assimilation and by
29 % compared with the simulation assimilating traditional observations
only (as shown in Fig. 5).</p>
      <p id="d1e1112">To the best of the authors' knowledge, SOCIB WMOP (<uri>https://www.socib.es/?seccion=modelling&amp;facility=forecast</uri>, last access: 9 May 2022) is presently the only
system in the Mediterranean Sea including an assimilation scheme of HFR data
in its operational chain.</p>
</sec>
<sec id="Ch1.S2.SS1.SSS3">
  <label>2.1.3</label><title>Short-term predictions</title>
      <p id="d1e1126">Assimilation of HFR data into models is still computationally expensive and
a complex issue, not to mention operational capabilities of such a
procedure. Because of these constraints, the availability of real-time
high-resolution HFR current fields has led to alternative solutions in order
to obtain short-term prediction (STP) of surface coastal currents through
the direct use of HFR historical and nowcast observations using different
approaches (e.g., Zelenke 2005; Frolov et al., 2012; Barrick et al., 2012;
Orfila et al., 2015; Vilibić et al, 2016).</p>
      <p id="d1e1129">The abovementioned studies develop and implement different STP approaches
(harmonic analysis of the last hours, genetic algorithms, numerical models,
etc.), which often require additional data or long training periods of data
without gaps. Hardware failures due to power issues, communications or
environmental conditions often result in spatiotemporal gaps within HFR
datasets. Spatial gaps can be filled on a real-time basis, but the filling of
long temporal gaps is not straightforward. Several gap-filling methodologies
have been developed for HFR datasets: open modal analysis – OMA
(implemented by Lekien et al., 2004, and further optimized by Kaplan and
Lekien, 2007), data-interpolating EOFs – DINEOF (Beckers and Rixen, 2003;
Alvera-Azcárate et al., 2005; Hernández-Carrasco et al., 2018b,
Bourg and Molcard, 2021), self-organizing maps – SOMs (Kohonen, 1982, 2000,
2001; Hernández-Carrasco et al., 2018b), reduced-order optimal
interpolation – ROII (Kaplan et al., 1997), optimal interpolation – OI (Kim
et al., 2008), artificial neural network – ANN (Ren et al., 2018),
variational analysis (Yaremchuk and Sentchev, 2011) and data-interpolating
variational analysis in <inline-formula><mml:math id="M27" display="inline"><mml:mi>n</mml:mi></mml:math></inline-formula> dimensions – DIVAnd (Barth et al., 2021). HFR-derived short-term predictions were developed by Zelenke (2005), Frolov et al. (2012), Barrick et al. (2012), Orfila et al. (2015), Solabarrieta et al. (2016), Vilibić et al, (2016) and Abascal et al. (2017). More
recently, Solabarrieta et al. (2021) developed a Lagrangian-based, empirical,
real-time, short-term prediction (L-STP) system in order to provide short-term forecasts of up to 48 h of ocean currents from HFR data.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F5"><?xmltex \currentcnt{5}?><?xmltex \def\figurename{Figure}?><label>Figure 5</label><caption><p id="d1e1141">Mean separation distance between virtual particles and drifters as
a function of the forecast horizon. Black represents the simulation
without DA (i.e., control run, CR). Blue stands for generic (GNR), which
assimilates data from satellite altimetry, SST and Argo profiles. Green and
red lines represent the simulation which assimilates HFR daily mean total
(TOT) and radial (RAD) observations, respectively, together with generic
observation sources. Original source: Hernández-Lasheras et al. (2021).</p></caption>
            <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f05.png"/>

          </fig>

      <p id="d1e1151">Through the NEURAL project (<uri>http://www.izor.hr/neural</uri>, last access: 9 May 2022), an
innovative neural-network-based ocean forecasting system has been developed,
providing gridded hourly surface current forecasts in the northernmost part
of the Adriatic for the next 72 h. The forecasting system uses an
unsupervised neural network algorithm, called self-organizing maps (SOMs, Kohonen,
1982; Liu et al., 2006), to train joint solutions coming from HFR
measurements and a numerical weather prediction model as hourly surface
currents and surface winds, respectively. Once the joint SOM solution has
been trained, the surface current forecast follows the predicted surface
winds that are the closest to the specific SOM solution (Fig. 6). Such a system
requires a strong relationship between the predictor (i.e., surface winds)
and the predictand (i.e., surface currents), which is largely found in
coastal regions of the Mediterranean, yet it can be applied for any other
combination of predictors and predictands. Also, high-frequency
processes such as tides are removed from the system as being minor to the
wind-driven dynamics, yet the tides can be added to the forecast.</p>
      <p id="d1e1157">The quoted northern Adriatic forecast system has been trained using 20 SOM
solutions (so-called Best Matching Units, Liu et al., 2006) on HFR data
measured between February and November 2008 conjoined with 3-hourly surface
winds interpolated to 1 h resolution coming from the Aladin/HR operational
model run once a day by the Croatian Meteorological and Hydrological Service
(Tudor et al., 2013). The forecasting system performance was tested in
the forecast (hindcast) mode during 2009 and 2010. Unfortunately, the HFR
system has had substantial problems since 2010 and the antennas were
eventually removed in the following years, resulting in a relatively short
dataset that is possibly not sufficient for strong reliability of the
forecasting system solutions. However, Vilibić et al. (2016) compared
this SOM-based surface current forecast system (available online in
<uri>http://jadran.izor.hr/neural/index.htm</uri>, last access: 9 May 2022) with the operational ROMS – Regional
Ocean Modelling System (Shñhepetkin and McWilliams 2003, 2005)
for the Adriatic, with the former lower showing biases and root mean square
errors.</p>
</sec>
</sec>
<sec id="Ch1.S2.SS2">
  <label>2.2</label><title>Extreme hazard coastal monitoring</title>
      <p id="d1e1172">Under the current climate-change scenario, no portion of the coastline is
safe from the threat of met-ocean hazards, which are expected to increase in
frequency, duration and virulence during the 21st century (Mitchell et
al., 2006; Stott, 2016). HFR constitutes a profitable asset for wise
decision-making since it presents a wide range of practical applications,
including the effective monitoring in near-real time of extreme coastal
hazards such as (i) extreme wind events, (ii) severe river discharges,
(iii) record-breaking storms and (iv) strong flow reversals (all
abovementioned events are addressed in Sect. 2.2.1.), (v) storm surges,
(vi) tsunamis (in Sect. 2.2.2), and (vii) typhoons and hurricanes (Barrick and
Lipa, 1986; Miles et al., 2017; Lipa et al., 2019).</p>
      <p id="d1e1175">In response to the increasingly frequent extreme events associated with
climate change, their detailed characterization by means of surface current,
wave and wind maps derived from HFRs may aid blue economy development
in coastal vulnerable areas of the Mediterranean region. Regardless of this,
the increasing retrieval of wave and wind maps derived from HFRs (Lorente
et al., 2022) is very relevant for the development of renewable ocean
energy, an emerging and innovative blue economy sector.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F6" specific-use="star"><?xmltex \currentcnt{6}?><?xmltex \def\figurename{Figure}?><label>Figure 6</label><caption><p id="d1e1180">The architecture of the SOM-based surface current forecasting
system in the northern Adriatic. Original source: from Vilibić et al. (2016).</p></caption>
          <?xmltex \igopts{width=398.338583pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f06.png"/>

        </fig>

<sec id="Ch1.S2.SS2.SSS1">
  <label>2.2.1</label><title>Extreme event monitoring</title>
      <p id="d1e1197">HFRs were used to investigate the upper ocean response to an extreme
wind event in the Ligurian Sea (NW Mediterranean) during October–November
2018, as described in Berta et al. (2020). This work focused on the analysis
of coastal sub-mesoscale structures, shaping surface currents and passive
transport. The authors estimate the pattern and magnitude of kinematic
properties (e.g., divergence and convergence as well as vorticity patterns) derived
from surface currents measured by the HFR-TirLig network (Fig. 1) to
characterize the evolution (before and after the event) of ocean scales at a
few kilometers.</p>
      <p id="d1e1200">During the storm, sea surface vorticity (Fig. 7, top panels) and divergence
(not shown but available in Berta et al., 2020) reach the order of the Coriolis
parameter <inline-formula><mml:math id="M28" display="inline"><mml:mi>f</mml:mi></mml:math></inline-formula>, indicating ageostrophic activity typical of sub-mesoscale
structures. The evolution of the sea surface structures suggested nonlinear
interactions with the wind forcing. Considering the time series of wind
speed and sea current properties (Fig. 7, lower panels) during and right
after the storm (around 29 October), current magnitude increased
approximately 4 times, while vorticity and divergence associated with the
small features almost doubled. Such abrupt changes in horizontal currents
and transport might also impact the vertical properties and in turn the
ecosystem.</p>
      <p id="d1e1210">In the delta of the Ebro River (NW Mediterranean), the HFR-Ebro system
observations have been crucial to capture the evolution of the most extreme
Ebro River freshwater discharge event registered over the last 15 years in
April 2018 (Ruiz et al., 2020). Results show the high impact of the
freshwater pulse discharged on the surface circulation pattern, exhibiting a
clear correspondence to high concentrations of satellite-derived
chlorophyll <inline-formula><mml:math id="M29" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> (Chl <inline-formula><mml:math id="M30" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> hereinafter) concentration. Hovmöller diagrams of
HFR-derived meridional and zonal currents indicate an increase in the
southeastward velocity during the period of extreme river discharge.
The proper representation of the basic oceanographic features of the
HFR-Ebro, as the Ebro River impulsive-type freshwater discharged, was
previously reported by Lorente et al. (2015).</p>
      <p id="d1e1227">This same region (i.e., Ebro Delta) was severely impacted by an
exceptional storm in (19–24) January 2020, which surpassed the 99th
percentile for several parameters (i.e., wind speed, significant wave height,
wave period and surface current velocity) compared with the climatology and
with a previous storm in January 2017. Particularly for this event, Lorente
et al. (2021) have assessed the ability of the HFR-Ebro to characterize
waves and currents under the record-breaking storm Gloria. By analyzing the
data from the HFR-Ibiza and HFR-Gibraltar, the authors have also evidenced
Gloria's remote effect in the Ibiza Channel and the Strait of Gibraltar,
altering the usual water exchanges between adjacent sub-basins. Furthermore,
the effect of Gloria was also manifested in the highest rates of particle
dispersion at the Ebro River mouth on 21 January.</p>
      <p id="d1e1231">As in the previous case, the HFR system strategically installed in the
Strait of Gibraltar (SoG) is considered an appropriate asset to effectively
monitor the Atlantic Jet (AJ) inflow (Lorente et al., 2019b) and the water
exchanges between the Atlantic Ocean and the Mediterranean Sea. The
classical picture of the surface circulation is characterized by current
pulses often exceeding 2 ms<inline-formula><mml:math id="M31" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> and time-averaged northeastward speeds
around 1 ms<inline-formula><mml:math id="M32" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> in the narrowest section of the SoG (Fig. 4a). Complete
collapse of the AJ and quasi-permanent inversion of the surface inflow
during prevalent intense easterlies is a singular phenomenon that deserved
detailed exploration (as previously mentioned in Sect. 2.1.2). Under this
temporal premise, a monthly Hovmöller diagram was computed for
HFR-derived zonal currents at the selected transect to easily detect a 2 d
full reversal episode during March 2017, represented by black boxes in Fig. 8a. The event detected consisted of an abrupt interruption of the eastward
inflow and complete reversal of the surface stream through the narrowest
section of the SoG (Fig. 8b). The circulation in the easternmost region of
the study domain was accelerated up to 0.8 ms<inline-formula><mml:math id="M33" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>, following clockwise
rotation that likely fed the Western Alboran Gyre (WAG), which was out of
the picture.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F7" specific-use="star"><?xmltex \currentcnt{7}?><?xmltex \def\figurename{Figure}?><label>Figure 7</label><caption><p id="d1e1272">From top to bottom: example map of normalized vorticity
before and during the extreme event. Time series of wind speed, surface current
magnitude, and root   mean square of normalized vorticity and divergence. Original source:
from Berta et al. (2020).</p></caption>
            <?xmltex \igopts{width=455.244094pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f07.png"/>

          </fig>

      <p id="d1e1281">The prevailing atmospheric synoptic conditions were inferred from ECMWF
predictions of sea level pressure and zonal wind at 10 m height (U10), as
shown in Fig. 8c–d. A significant latitudinal gradient of sea level
pressure was observed, with high pressures over the Gulf of Biscay and
isobars closely spaced in the SoG, leading to extremely intense easterlies
(above 10 ms<inline-formula><mml:math id="M34" display="inline"><mml:mrow><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup><mml:mo>)</mml:mo></mml:mrow></mml:math></inline-formula> channeled through the strait due to its specific
geometric configuration. Therefore, high pressures and intense, permanent
and spatially uniform easterlies prevailed over the entire study domain,
inducing westward outflow through the SoG as revealed by the 2 d
averaged HFR circulation maps. Local wind forcing at this scale seemed to
play a primary role in explaining such AJ collapse and the related inflow
reversals, in agreement with previous studies (Garret, 1983;
García-Lafuente et al., 2002; Menemenlis et al., 2007; Péliz et
al., 2009; Reyes et al., 2015; Lorente et al., 2019b, Bolado-Penagos
et al., 2021).</p>
</sec>
<sec id="Ch1.S2.SS2.SSS2">
  <label>2.2.2</label><title>Tsunami detection</title>
      <p id="d1e1307">Tsunami early warning and alert represent an emerging and promising application of
HFR. The main principle underlying the detection is that the abnormal
surface current pattern induced by the orbital velocity of the tsunami wave
train can be measured and interpreted in real time by an appropriate
detection algorithm. The idea was first proposed by Barrick (1979), but it
was only after the 2004 Indian Ocean disaster that the proof of concept was
made on the basis of actual HFR data. It was shown numerically with
simulated (e.g., Lipa et al., 2006; Gurgel et al., 2011) and real (e.g., Lipa
et al., 2011, 2012; Dzvonkovskaya et al., 2012) events that the tsunami
signature could be clearly seen in the HFR radial currents, and some
appropriate detection algorithms were proposed. One strong point of HFR
tsunami detection is that it is not bound to the nature of the source (i.e.,
seismic or atmospheric) and can be used as a useful complement to other
warning systems in places where those are either not available or
non-effective. Today, more than 20 real tsunamis have been detected
“offline” with the reanalysis of HFR data. In view of the growing interest
in these new capabilities of HFR, some radar manufacturers now provide
commercial toolboxes along with their hardware system for the early
detection of tsunamis; such systems have been installed in some places at
risk (e.g., Vancouver Island, Canada; Oman; New Jersey, USA; Sagres in SW
Portugal). To date, the only real-time detection was issued following a
meteotsunami that occurred on  1 October 2016 in Tofino, BC,
Canada (Dzvonkovskaya et al., 2017; Guérin et al., 2018).</p>
      <p id="d1e1310">However, no such HFR tsunami alert system has yet been installed in the
Mediterranean Sea, even though there is a non-negligible tsunami hazard in
this region, as witnessed by very destructive co-seismic events in recent
history (e.g., Messina, Sicily, 1908). Some worst-case scenarios with a
strong (<inline-formula><mml:math id="M35" display="inline"><mml:mrow><mml:msub><mml:mi>M</mml:mi><mml:mn mathvariant="normal">7.8</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>) earthquake on the northern Algerian margin predict important
tsunami waves with 3–4 m amplitude on the French–Italian Riviera (BRGM,
2007). Moderate earthquakes such as the <inline-formula><mml:math id="M36" display="inline"><mml:mrow><mml:msub><mml:mi>M</mml:mi><mml:mn mathvariant="normal">6.9</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> 21 May 2003 Boumerdes–Zemmouri
are sufficient to cause 1–3 m amplitude harbor oscillations within 40–60 min in the Balearic Islands, which would be the most impacted spot by
seismic sources in northern Algeria (Wang et al., 2005; Sahal et al., 2009).
The impact on the French Mediterranean coast impacted by a seismic source on
the northern Algerian margin is shown in Fig. 9.</p>
      <p id="d1e1335">In addition to co-seismic tsunamis, frequent meteotsunamis (i.e., tsunamis of
meteorological origin) have been reported in the Balearic Islands, named
– “rissaga” (Jansa, 2007), Adriatic Sea – “šćiga” (Vilibić
and Šepić 2009; Orlić, 2015), Sicily Channel – “marrobbio”
(Candela et al., 1999; Zemunik et al., 2021), Malta – milg<inline-formula><mml:math id="M37" display="inline"><mml:mi mathvariant="normal">ℏ</mml:mi></mml:math></inline-formula>uba”
(Drago, 2008), northern Persian Gulf (Kazeminezhad et al., 2021), Black Sea
(Vilibić et al., 2021) and Aegean Sea (Papadopoulos, 1993). Even though
these events have limited regional impact, they can cause severe local
damage in harbors and bays due particularly to the micro-tidal regime,
resulting in rapid sea level changes (Vilibić et al., 2021). Indeed, the
strongest known meteotsunami in the Mediterranean Sea (and likely in the
world) was in the Adriatic, the so-called Great Vela Luka Flood (June 1978),
with an amplitude of 6 m and periods of about 20 min, as detailed by
Vučetić et al. (2009), closely followed by the event from Ciutadella
Harbor (Menorca island, Spain) in June 2006 (Jansa et al., 2007) with 4–5 m
of amplitude. Meteotsunamis are caused by atmospheric disturbances combined
with several further possible amplification mechanisms of the induced sea
surface wave; these are mostly the so-called Proudman, Greenspan and shelf
resonances in coastal areas, which can lead to strong harbor resonances in
semi-closed basins (Orfila et al., 2011). Today, the generation of these
meteotsunamis is better understood (Monserrat et al., 2006; Šepić et
al., 2009, 2015; Vilibić and Šepić 2009; Ličer et al., 2017),
but their prediction is still a very challenging task (Denamiel et al.,
2019, Romero et al., 2019, Mourre et al., 2020).</p>
      <p id="d1e1345">When located in the areas affected by meteotsunamis, HFR-based tsunami
early warning systems could be a useful complement to these forecasting
systems, helping to issue specific alerts on the basis of the actual observed
surface currents 20–40 km offshore a few minutes before the generation of
extreme sea level oscillations. Note that tsunami early warning systems
only require software updates of existing HFR and could be installed at
reduced cost in some places. However, some strategic spots are not covered
yet and would need a novel installation to monitor the travel directions
of incoming waves from the most probable sources (northern Algerian earthquake,
western Corsica submarine mass failure, northern Ligurian earthquake, etc.).
Another related issue is extending the range of these HFRs, which would imply
operating at lower-frequency bands (4–5 or 9 MHz) than those usually
employed in the Mediterranean region (13, 16 or 25 MHz). An HFR prototype
(i.e., Stradivarius radar) operating at 4.5 MHz with 200–300 km range was
developed by Diginext Ltd. a few years ago for the Gulf of Lion as a
proof of concept (Grilli et al., 2015). Such HFR systems can serve the
double purpose of warning and characterizing abnormal surface current
patterns arising from tsunami-like waves of seismic or atmospheric origin.
As recently suggested by Domps et al. (2020), they can also be used as
proxies for the observation of low-pressure fronts of atmospheric gravity
waves that could lead to storm surge, if not meteotsunamis.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F8"><?xmltex \currentcnt{8}?><?xmltex \def\figurename{Figure}?><label>Figure 8</label><caption><p id="d1e1351"><bold>(a)</bold> Monthly Hovmöller diagram of HFR-derived zonal current
speed at the selected transect (shown in Fig. 4a). Red (blue)
represents eastward (westward) surface flow. A 2 d episode of permanent
flow reversal is marked (14–15 March). <bold>(b)</bold> HFR-derived mean surface
circulation for 14–15 March 2017: permanent flow reversal. <bold>(c–d)</bold> 2 d mean
sea level pressure and zonal wind at 10 m height (<inline-formula><mml:math id="M38" display="inline"><mml:mrow><mml:msub><mml:mi>u</mml:mi><mml:mn mathvariant="normal">10</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>), respectively, as
provided by the ECMWF: intense and persistent easterlies were the driver of
the flow reversal. Original source: from Lorente et al. (2019b).</p></caption>
            <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f08.png"/>

          </fig>

</sec>
</sec>
<sec id="Ch1.S2.SS3">
  <label>2.3</label><title>Environmental transport processes</title>
      <p id="d1e1388">In the Mediterranean, as elsewhere in the world, the coastal zones serve as
the main entry point of nutrients, pollutants and sediments into the ocean,
with the multi-scale coastal ocean dynamics being the key drivers for their
transport, also impacting their dispersal and retention as well as the cross-shelf
exchanges. HFRs have demonstrated a capacity to provide very valuable
measurements to continuously monitor the mesoscale structures and frontal
dynamics that organize the coastal surface flow and associated transport through
the developments in the understanding of Lagrangian dynamics from HFR data
(Rubio et al., 2020). The comprehension of the coastal ocean conditions and
variability underlying ocean productivity that correlate with fish stock
abundance, fish recruitment in coastal areas, and dispersion and retention of
larvae  is critical for sustainable management of fisheries
resources (Sciascia et al., 2018). Coastal and littoral areas are also very
vulnerable target regions for pollution in terms of environmental and
ecosystem impact as well as economic and societal consequences, also being
essential to assist water quality management by tracking the source and drift of
contaminants (e.g., chemical, sewage, oil spills or harmful algal blooms). In
the Mediterranean Sea, the applicability of HFRs in the study of
environmental transport processes is particularly relevant due to its
limited exchange with the oceanic basins, its microtidal character, and its
intense internal mesoscale and sub-mesoscale circulation. These specific
characteristics of this semi-enclosed sea reduce the potential of dilution
and dispersion of dissolved and particulate waste, maximizing the impact of
one of the most commonly identified threats (i.e., marine litter and
contaminants). In addition, despite being considered one of the most
oligotrophic areas in the world ocean, it is also one of the world's hot
spots for biodiversity (Coll et al., 2010, Gabrié, et al., 2012),
providing vital areas for the reproduction of pelagic species (e.g., Atlantic
bluefin tuna, white shark and sea turtles) and hosting sensitive ecosystems
in the shallow coastal waters (e.g., seagrass meadows of the endemic
<italic>Posidonia oceanica</italic>, the key intertidal habitat of vermetid reefs built by endemic gastropod
<italic>Dendropoma petraeum</italic> and  coralligenous assemblages, as detailed by Coll et al., 2010).</p><?xmltex \hack{\newpage}?>
<sec id="Ch1.S2.SS3.SSS1">
  <label>2.3.1</label><title>Pollution and floatable tracking</title>
      <p id="d1e1405">Coastal regions in the Mediterranean Sea are heavily inhabited, with strong
tourism pressure and maritime activity resulting in human and industrial
waste intentionally or accidentally dumped into coastal waters. These
pollutants evolve according to their chemical transformation over time,
are caught in the 3D general circulation, and are carried offshore and to other
distant coastal areas by currents. For example, heavy metals or other
chemical contaminants that may be present in semi-enclosed harbors (Tessier
et al., 2011) could have important consequences for the ecosystem, and
plastic litter is currently a massive and particularly harmful component (e.g.,
Ryan et al., 2009; Declerck et al., 2019) of the marine pollution in the
Mediterranean Sea.</p>
      <p id="d1e1408">Furthermore, detecting, monitoring and cleaning up oil slicks following an
offshore spill before they reach the coast is a major challenge.
Consequently, monitoring, understanding and forecasting coastal dynamics are
critical steps to develop adequate strategies to mitigate the effects of
pollution in marine environments from or towards coastal areas. However,
forecasting coastal dynamics is one of the most challenging issues in
geosciences due to their strong space–time variability as well as the
complexity of the processes controlling the dynamics that interact
simultaneously over a broad range of time–space scales, as previously
highlighted in Sect. 2.1.2. Thanks to the growing importance of HFR as a key
element of coastal observing systems, coastal currents can nowadays be
continuously measured in relatively large coastal areas, thus enabling the
analysis of transport properties of the surface flow by means of different
diagnostics based on the Lagrangian approach (i.e., addressing the effects of
the spatiotemporal variability of the velocity field on drifted particles
or tracers). Recent studies have demonstrated the potential of this
land-based remote sensing technology for different applications in the field
of tracking oil spills (Abascal et al., 2009), marine litter (Declerck et
al., 2019) or phytoplankton (Hernández-Carrasco et al., 2018a).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F9"><?xmltex \currentcnt{9}?><?xmltex \def\figurename{Figure}?><label>Figure 9</label><caption><p id="d1e1413">Map of the French Mediterranean coast (close to the HFR-Tln
system) within the simulated surface elevation (in meters) after 1 h 10 min
propagation for a tsunami generated by a <inline-formula><mml:math id="M39" display="inline"><mml:mrow><mml:msub><mml:mi>M</mml:mi><mml:mn mathvariant="normal">7.8</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula> seismic source on the northern
Algerian margin. The numerical simulation uses FUNWAVE-TVD software with three
nested grids in the western Mediterranean basin (courtesy of Stephan Grilli,
University of Rhode Island, USA).</p></caption>
            <?xmltex \igopts{width=227.622047pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f09.png"/>

          </fig>

      <p id="d1e1434">In this regard, the trajectories of passive tracers are determined by the
velocities measured by HFR (e.g., Ullman et al., 2006), often including the
effect of subgrid-scale diffusion. When chemical pollutants are considered,
additional processes should be included. For instance, when simulating oil
spill trajectories, the advection term is a linear combination of the
surface current velocity, the wind velocity and the stokes drift, and
spreading, evaporation and emulsification should be included in the
transport model.</p>
      <p id="d1e1437">Here we provide evidence to support the reliability of HFR currents for
tracking substances in coastal areas. The Lagrangian validation has been
performed using data from eight drifter trajectories available in the domain
of the HFR area of coverage in the Ibiza Channel (HFR operated by SOCIB,
Tintoré et al., 2013, 2020) during October 2012. We use the HFR velocity
fields to compute the Lagrangian coherent structures (LCSs), which are very
suitable to provide a template of the fluid flow transport (see Haller,
2015, and references therein), allowing the detection of transport barriers,
which are of great relevance for marine dynamics. For example, LCS obtained
from ridges of the finite-size Lyapunov exponents have been correlated with
filaments of remotely sensed Chl <inline-formula><mml:math id="M40" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> (Lehahn et al., 2007;
Hernández-Carrasco et al., 2014, 2018a, 2020), sea bird foraging
behavior (Tew Kai et al., 2009), the modeled extension of oxygen
minimum zones (Bettencourt et al., 2015) and wind forcings (Berta et al., 2014b). At coastal scales, the dynamical picture in the Lagrangian frame
has been analyzed using data from HFR currents to identify relevant
small-scale transport barriers (Lekien et al., 2005; Gildor et al., 2009;
Rubio et al., 2018), some of them focusing on coastal areas of the
Mediterranean Sea (Haza et al., 2010; Berta et al., 2014b;
Hernández-Carrasco et al., 2018a). Figure 10 shows the evolution of a set
of virtual neutrally buoyant particles initially deployed on the northern
(blue dots) and southern (black dots) flank of a given LCS measured from the
HFR-Ibiza on 25 January at 17:00 UTC in 2013 (Fig. 10a). Although the
location and magnitude of this LCS evolve in time, the LCS persists for
several hours, manifesting the presence of a coherent transport barrier
preventing the two sets of particles from being mixed up. A meridional LCS is formed
and maintained during the simulated period, limiting water exchanges between
the coast and the open ocean (Fig. 10a–c).</p>
      <p id="d1e1447">Another example of application of the Lagrangian properties derived from
HFR focuses on the monitoring of the physical mechanisms that can influence
the escape times of mesotrophic and/or polluted coastal waters to
oligotrophic offshore areas, as described in Rubio et al. (2020). Using as
input gap-filled HFR velocity fields a Lagrangian particle-tracking model
provides the particle trajectories. From the Lagrangian model outputs, it is
possible to infer the characteristic timescales for transport processes in
the HFR footprint area by means of the escape rate of active particles (Fig. 11). Thus, HFR is shown to be an excellent tool to monitor conditions and
identify the different scenarios that favor the local retention and
dispersal of shelf waters in two study areas under the influence of ocean
boundary currents.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F10" specific-use="star"><?xmltex \currentcnt{10}?><?xmltex \def\figurename{Figure}?><label>Figure 10</label><caption><p id="d1e1452">Evolution of two sets of particles (black and blue) in the area
covered by the HFR-Ibiza in January 2013 superimposed on the backward finite-size Lyapunov exponent – FSLE
(color bar). The virtual particles are initially deployed at both sides of a
barrier revealed by a zonal LCS on 25 January 2013 at 17:00 evolving for 68 h.</p></caption>
            <?xmltex \igopts{width=497.923228pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f10.png"/>

          </fig>

</sec>
<sec id="Ch1.S2.SS3.SSS2">
  <label>2.3.2</label><title>Eddy tracking</title>
      <p id="d1e1469">Ocean eddies are ubiquitous, pervasive flow structures which dominate the
ocean velocity field at several scales from the mesoscale to the local scale
(Chelton et al., 2011). They play a fundamental role in sea dynamics, being
responsible for the energy transfer among different scales (down to the
dissipative range) as well as for their ability to transport nutrients,
biomass, sediments and pollutants. Mesoscale eddies, produced by geostrophic
instabilities, are not able to advance the energy transfer, being
constrained by geostrophic and hydrostatic balance (Charney, 1971). When the
balance is broken, the downscale may continue through inertia–gravity waves
emitted from currents, ageostrophic instabilities and bottom boundary layer
turbulence, which are responsible for the formation of sub-mesoscale eddies.
At a lower scale, three-dimensional turbulence proceeds toward the
dissipative range (McWilliams, 2019).</p>
      <p id="d1e1472">The presence of ocean eddies has become more evident in recent years thanks
to the introduction of new oceanographic measurement techniques, while their
exhaustive characterization would require synoptic time series of the
velocity field in the ocean (Robinson, 1983). Such synoptic observations are
made available only through satellite data. However, besides being limited
to relatively large scales and preferably to the open ocean, they do not
provide direct measurements of the total velocity field. Indeed, altimetry
data can be used to retrieve the surface geostrophic field, which lacks a
possibly important portion of the dynamics (Rinaldi et al., 2010; Conti et
al., 2016). Other ways to observe eddies from satellites consist of the
observation of their presence in the sea surface temperature or in the
tracer field patterns, as displayed by ocean color (Robinson, 2010). Coastal
HFRs overcome all the above limitations, enabling the detection and
tracking of the time history of surface eddies down to sub-mesoscale at the
cost of a reduced spatial extent.</p>
      <p id="d1e1475">Mandal et al. (2019) provide quite an extensive list of recent literature
reporting sub-mesoscale features observed by HFRs, with examples of
observations in various coastal areas from the Atlantic to the Pacific and
Indian oceans (Shay et al., 1995, 2000; Kirincich, 2016b; Archer et al.,
2017; Lai et al., 2017; Arunraj et al., 2018). It is worth noticing that such
features may have a strong vertical signature that HFR data fail to account
for and therefore need to be complemented by further information
spanning from direct measurements of the horizontal and vertical velocity
profile to indications indirectly derived from, e.g., satellite turbidity
measurements (see discussion in Uttieri et al., 2011).</p>
      <p id="d1e1478">A vast HFR network now covers the northwestern Mediterranean coastal areas
(see Lorente et al., 2022), which is characterized by significant mesoscale
variability and eddy generation that, in some cases, shows recursive and
seasonal patterns. Allou et al. (2010) used HFR to observe and characterize
vortex structures, mostly anticyclonic, in the Gulf of Lion. They also
argued they were correlated with specific wind patterns. Schaeffer et al. (2011) improved the analysis and employed both HFR measurements and
numerical modeling to analyze the eddy-generating mechanism. They found it
is primarily influenced by wind forcing and its interaction with topographic
constraints (northerly offshore wind), as well as freshwater input from the Rhone river
(southerly onshore wind). The combination of HFR, in situ observations and
modeling tools allowed Guihou et al. (2013) to identify an anticyclonic
coastal eddy which was generated in front of Nice by a meander of the
Northern Current and advected downstream toward the Toulon area,
interacting with the mean circulation. More recently, the analysis of the
long 2012–2019 HFR time series in Toulon allowed identification of cyclonic and
anticyclonic recurrent eddies mainly generated by wind and boundary current
undulations (Bourg and Molcard, 2021).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F11" specific-use="star"><?xmltex \currentcnt{11}?><?xmltex \def\figurename{Figure}?><label>Figure 11</label><caption><p id="d1e1484">Maps of particle residence times (hours) computed for different
dates and seasons from HFR observations in the Ibiza Channel SOCIB (<bold>a, b</bold> for
winter and <bold>c</bold> for summer conditions). Original source: from Rubio et al. (2020).</p></caption>
            <?xmltex \igopts{width=497.923228pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f11.png"/>

          </fig>

      <p id="d1e1499">The development of monitoring networks providing long time series of data
is making automatic eddy detection methods more and more topical and
important. Generally speaking, existing eddy detection algorithms can be
divided into three families: (i) those that are based on the geometrical
features of the velocity field, typically in terms of streamline closedness,
winding angle or vector geometry (Sadarjoen et al. 1998; Heiberg et al., 2003; Ebling and Scheuermann 2003; Nencioli et al., 2010); (ii) those based
on dynamical characteristics, such as parameters quantifying the eddy
intensity and its vorticity (Jeong and Hussain 1995; Fang and Morrow
2003; Isern-Fontanet et al., 2003; Morrow et al., 2004); (iii) and hybrid
methods based on the combination of geometric and dynamical criteria
(Mkhinini et al., 2014; Conti et al., 2016, see also the extensive review in
the paper by Le Vu et al., 2018).</p>
      <p id="d1e1502">Algorithms specifically devised for HFR data are very few. The methods
tested in the Mediterranean Sea (Caldeira et al., 2012) are limited to those
by Nencioli et al. (2010) and Bagaglini et al. (2020). The former, even
though developed for HFR data (and for high-resolution numerical model
outputs), has found a widespread range of applications to observations
collected by different platforms, as witnessed by current oceanographic
literature (Liu et al., 2012; Dong et al., 2014). It is a method based on
the geometry of the velocity vectors. It was conceived for geostrophic or
quasi-geostrophic recirculating features showing very little divergence.
For this reason, it is very suitable to describe mesoscale eddies but may
fail in detecting sub-mesoscale ones, which often are characterized by
divergence or convergence and by a high degree of deformation of the
velocity field geometry. YADA (Yet Another eddy Detection Algorithm), developed by Bagaglini et al. (2020), was conceived specifically to
overcome this limitation and be utilized to automatically detect
sub-mesoscale eddies, which may exhibit highly non-geostrophic
characteristics. It is a hybrid method, which focuses on both the dynamical
and geometric features of the velocity field, first identifying the local
extrema of a dynamical field characterizing recirculations (e.g., the local
normalized angular momentum, see Mkhinini et al., 2014; the Okubo–Weiss
parameter, Okubo, 1970; Weiss, 1991), similarly to the first step from AMEDA
(Angular Momentum Eddy Detection and tracking Algorithm) defined by Le Vu et al. (2017), and thereafter analyzing the streamline geometry in a
neighborhood of the extremum. YADA (Bagaglini et al., 2020) has been
successfully applied to 1 km resolution HFR data from the Gulf of Naples,
showing its ability to identify strongly asymmetric, convergent or divergent
sub-mesoscale eddies. Its application to coastal HFR data from other areas of
the western Mediterranean is presently under way.</p>
      <p id="d1e1505">The HFR system from the LaMMA Consortium (described in Lorente et al., 2022)
covers part of the Ligurian Sea and the Tuscany Archipelago, which is a
shallow area separating the Ligurian and Tyrrhenian basins, bordering
the Corsica Channel eastward, with complex topography and coastal
morphology, also due to the presence of several islands (Elba, Capraia,
Montecristo, Gorgona). Sea dynamics are strongly influenced by seasonality
and characterized by the presence of the Tyrrhenian boundary current and its
bifurcation, the Eastern Corsica Current (Astraldi and Gasparini, 1992;
Millot, 1999; Vignudelli et al., 2000). Through drifters, in situ data and a
numerical model, Poulain et al. (2020) studied the area in the summer
season. They found prevailing southward current flowing next to the Italian
coast, then turning westward and northward, encountering Elba island. A
further eastward motion led to the formation of an anticyclone centered on
Capraia island, which exhibited variations correlated with wind forcing. The
presence of an anticyclone north of the Corsica Channel in summer and autumn
seasons was previously documented by Ciuffardi et al. (2016) by means of
in situ profiles and altimetric data. Furthermore, they argued that the
characteristics of the anticyclone (position and size) may affect the
general circulation by isolating the Tyrrhenian and Ligurian basins, mostly
in summer. These hydrodynamics features can influence the concentration of
floating marine litter, which was shown to be particularly high in certain
periods of the year (Fossi et al., 2017).</p>
      <p id="d1e1508">Here, we show the application of both YADA and the Nencioli et al. (2010)
algorithms to the surface currents derived from the HFR-LaMMA system
during the year 2019.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F12" specific-use="star"><?xmltex \currentcnt{12}?><?xmltex \def\figurename{Figure}?><label>Figure 12</label><caption><p id="d1e1514">Maps of the area of the eastern Ligurian Sea and Tuscany Archipelago
showing the HFR-derived surface currents (colored arrows indicate the
current speed) and the detection of four eddies in early August 2019 by
YADA. The blue star marks the eddy center.</p></caption>
            <?xmltex \igopts{width=455.244094pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f12.png"/>

          </fig>

      <p id="d1e1523">Figure 12 reports four eddies detected by YADA and the
corresponding surface currents in August 2019.</p>
      <p id="d1e1526">Figure 13 shows the results of the application of the algorithm by Nencioli et al. (2010) to the whole year 2019, which provided a seasonal census of
anticyclonic and cyclonic eddies in the area sampled by the HFR-LaMMA
system. The HFR coverage was not uniform during the year, with generally
lower percentages for the warmer seasons (i.e., spring, summer). The area
north of Elba island was characterized by the highest eddy activity
throughout the year, with a predominance of anticyclonic eddies in colder
seasons and a clustered pattern in summer, showing anticyclonic eddies east
of Capraia island and cyclonic ones toward the coast.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F13" specific-use="star"><?xmltex \currentcnt{13}?><?xmltex \def\figurename{Figure}?><label>Figure 13</label><caption><p id="d1e1531">Maps of the area covered by the LaMMA HFR network showing the
percentage of HFR data availability during 2019 for <bold>(a)</bold> winter, <bold>(b)</bold> spring, <bold>(c)</bold> summer and <bold>(d)</bold> autumn. The Tuscany Archipelago (i.e., Elba island) is at the
lower right corner of the figures. Tracked cyclonic (black) and anticyclonic
(red) eddies detected in each season are overlaid.</p></caption>
            <?xmltex \igopts{width=312.980315pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f13.png"/>

          </fig>

      <p id="d1e1552">The number of detected eddies depended also on the availability of HFR data;
indeed, a smaller number of eddies was found in spring (28) with respect to
the other months (62 winter, 68 summer, 62 autumn). Median eddy life span
was around 1.125 d for all seasons except in spring, although some were
able to survive up to 6 d.</p>
      <p id="d1e1556">Although the present work is preliminary, it may lay the foundation for a
detailed analysis concerning the seasonal features of eddy activity within
the Tuscany Archipelago and its effect on the general circulation. Surface
currents from HFR can be combined with numerical model outputs to
bridge the gap relative to the spatial and temporal coverage of data and to
improve the representation and forecast of the real sea state: HFR
observations enhance numerical simulations by resolving fine-scale processes
in intricate regions with complex geometry configurations. In turn,
hydrodynamic models can reciprocally serve as integrative connectors of
sparse in situ observations and gappy HFR surface current maps by offering a
seamless predictive picture of the three-dimensional ocean state.</p>
</sec>
<sec id="Ch1.S2.SS3.SSS3">
  <label>2.3.3</label><title>Transport of biological quantities and connectivity</title>
      <p id="d1e1568">The necessity to preserve the marine ecosystem equilibrium and the water
quality has fostered the use of HFR data in supporting coastal zone
management and assessing the variability in the dynamics of marine
ecosystems. In particular, HFR data have been used worldwide to address
ecological and water quality issues such as (i) to understand the transport
and retention processes of plankton or wastewater discharge in some regions
of NW Spain (Ria de Vigo) (Piedracoba et al., 2016) and the western
Mediterranean (Hernández-Carrasco et al, 2018a), at coastal upwelling
fronts off central California (Bjorksted and Roughgarden, 1997) and in
Monterey Bay (Coulliette et al., 2007); (ii) to investigate the enhancement
of productivity due to the retention of phytoplankton within the flow in the
Santa Barbara Channel (Brzezinski and Washburn, 2011); and (iii) to analyze
the relationship between populations of larval and juvenile fishes and the
mesoscale flow field in the California Current System (Nishimoto and
Washburn, 2002).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F14" specific-use="star"><?xmltex \currentcnt{14}?><?xmltex \def\figurename{Figure}?><label>Figure 14</label><caption><p id="d1e1573"><bold>(a)</bold> Map of the Gulf of Naples (southern Tyrrhenian Sea) showing
the <bold>(a)</bold> Lagrangian backtracking trajectories of virtual phytoplankton
patches (VPPs) in the period 3–7 June 2009  and <bold>(b)</bold> main origin sectors
of the VPPs at the LTER-MC site resulting from backward simulations; index
sectors of VPPs are 1–2–3–4–5 for coastal areas and 6–7–8 for offshore
areas. <bold>(c)</bold> Comparison among backtracked Lagrangian origin and ecological
analysis based on salinity and Chl <inline-formula><mml:math id="M41" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> data measured weekly at LTER-MC. Green: VPPs originating from coastal areas; blue: VPPs originating from
offshore areas; red: VPPs originating partly from coastal and partly from
offshore areas. Adapted from Cianelli et al. (2017).</p></caption>
            <?xmltex \igopts{width=455.244094pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f14.png"/>

          </fig>

      <p id="d1e1600">Here we present examples of application of HFR data to investigate
ecological questions in three Mediterranean coastal areas: the Gulf of
Naples (GoN, Tyrrhenian Sea), the Gulf of Manfredonia (GoM, western Adriatic
Sea) and the Malta–Sicily Channel (mid-Mediterranean Sea).</p>
      <p id="d1e1604">In the GoN, continuous observations of the HFR current fields
highlighted several characteristics of the surface circulation and water
exchange between the interior of the gulf and the neighboring open
Tyrrhenian Sea (Cianelli et al., 2013). An oscillating plankton population
dynamic has also been frequently observed in the GoN, at Long-Term
Ecological Research station MareChiara (LTER-MC), where plankton abundance
has been monitored weekly since 1984. A proof-of-concept study (Cianelli et al.,
2017) was thus conducted in order to characterize the spatial scales and
the provenance of phytoplankton assemblages detected at LTER-MC and to
dissect processes regulating plankton dynamics.</p>
      <p id="d1e1607">The study focused on a year-long analysis carried out for 2009, which was
characterized by a very accurate estimate of the surface dynamics, with a
reduced number of gaps among ecological measurements and HFR data. The
approach followed these conceptual steps: (i) reconstruction of the annual
and seasonal regimes of HFR currents detected at the LTER-MC site and (ii) computation of Lagrangian backtracking simulations advecting virtual
phytoplankton patches (VPPs) in the HFR field (Fig. 14a). VPPs were
released at the LTER-MC site on the dates of the weekly oceanographic campaigns
and tracked backward, thus allowing the estimation of the positions of the
VPPs up to 4 d (i.e., 96 h) prior to arrival at LTER-MC. The next step was (iii)
identification of the prevailing directions from which the VPPs arrive at the
LTER-MC site as resulting from backtracking simulations (Fig. 14b), also
allowing the definition of the spatial distribution of the VPP origin zones
(not shown) in the GoN. This was followed by (iv) comparison among backtracked Lagrangian
reconstruction and ecological analysis based on salinity and Chl <inline-formula><mml:math id="M42" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> data
obtained through weekly sampling at LTER-MC (Fig. 14c) as well as (v) identification
of different modes of coupled physical and ecological functioning in the GoN
as resulting from physical transport and biological processes (“allogenic”
and “autogenic” factors, respectively).</p>
      <p id="d1e1617">The results showed an alternation in plankton dynamics between phases
reflecting the influence of coastal (green) and offshore (blue) circulation
patterns on the biological community. The phytoplankton community detected
at LTER-MC generally originated from the coast, whereas the offshore inflow
marginally changed the main traits of phytoplankton assemblages.
Backtracking simulations and biological data strictly agree, highlighting
that the plankton community at LTER-MC during 2009 was affected by the
alternation of coastal and offshore influence.</p>
      <p id="d1e1620">Biological autogenic factors drive the modifications of coastal
phytoplankton communities during coastal “green” phases, thus suggesting
that the GoN tends to retain the same communities via coastward
circulation, especially during summer. Physical allogenic factors are
important in driving dilution and species advection of coastal
phytoplankton during the offshore “blue” phase. This marked alternation
between coastal and offshore water masses acts to promote phytoplankton
diversity because the dilution in the phytoplankton density may decrease
the impact of the dominating species over the available resources.</p>
      <p id="d1e1623">The integration of long-term biological data and high-resolution current
fields represents an optimal tool to investigate the role of surface
circulation in structuring the marine plankton community, thus confirming
the value of HFR systems to analyze the seasonal fluctuations in marine
ecosystems dynamics and to unveil the mechanisms of coastal connectivity.</p>
      <p id="d1e1626">The GoM is a well-known recruitment area in the Adriatic Sea (Sciascia et
al., 2018; Corgnati et al., 2019a). In this region, HFRs have been used to
understand the role of ocean currents in the recruitment of small pelagic
fishes (i.e., European sardines, <italic>Sardina pilchardus</italic>). Figure 15 shows residence times within the
GoM, estimated using trajectories of virtual drifters computed from the
surface currents measured by HFRs. Months with high (October) and low (February)
residence times are associated with weaker and stronger surface currents in the
central area of the gulf. The relatively short (<inline-formula><mml:math id="M43" display="inline"><mml:mrow><mml:mo>&lt;</mml:mo><mml:mn mathvariant="normal">12</mml:mn></mml:mrow></mml:math></inline-formula> d) average
residence times have shown that local spawning is less likely to take place
than transport to the gulf from remote spawning areas through advection
pathways. Results agree with otolith measures, suggesting that the arrival
of larvae within the gulf is characterized by repeated pulses from remote
spawning areas that are likely to play a fundamental role in maintaining the
nursery.</p>
      <p id="d1e1643">The Malta–Sicily Channel is both the most fished area in western
Mediterranean Sea and a very important hot spot of biodiversity (Médail
and Quézel, 1999). In this region, Capodici et al. (2018) combined the
HFR-CALYPSO surface currents together with satellite images of Chl <inline-formula><mml:math id="M44" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> and
SST to explain physical driving mechanisms that can help interpret ocean
productivity and plan maritime activities in a more adaptive and proactive
way. On the one hand, as mentioned by the authors, monitoring water quality
data provides valuable insight into the understanding of processes driving
spatial and temporal changes in productivity at sea (Behrenfeld et al.,
2006). Chl <inline-formula><mml:math id="M45" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> and SST are generally accepted as proxies for water quality and
are very helpful to detect upwelling events, which frequently occur
along the Sicilian coast. In particular, sea currents are responsible for
dispersion, transport or retention of nutrients among which Chl <inline-formula><mml:math id="M46" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> is widely
used as a proxy variable; moreover, current jets or eddies are often
observable as cold or warm areas in SST maps, respectively. Even if both
Chl <inline-formula><mml:math id="M47" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> and SST maps are usually retrieved by means of satellite data maps,
cloudiness often reduces the satellite data availability; thus, temporal
aggregated products (e.g., at 8 or 16 d) are the only data available. In
this framework, the integration of sea surface current data provided by HFRs
can fill the gap of knowledge due to the inadequate temporal (and sometimes
spatial) resolution of these water quality maps. Capodici et al. (2018)
used principal component analysis – PCA (Preisendorfer, 1988) to firstly
extract the dominant spatial patterns of these variables in 2013 (Fig. 16,
left panels) and to secondly quantify the degree of correlation between SST
(or Chl <inline-formula><mml:math id="M48" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula>) and HFR-derived surface current spatiotemporal patterns (see
Fig. 16, bottom right panel). The spatial correlation analysis suggests the
importance of current advection in phytoplankton transport, being
characterized by fringes where very high positive correlation areas are
surrounded by very high negative ones and vice versa.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F15" specific-use="star"><?xmltex \currentcnt{15}?><?xmltex \def\figurename{Figure}?><label>Figure 15</label><caption><p id="d1e1683">Maps of the Gulf of Manfredonia showing monthly bootstrap
estimates of average residence times (in days) of virtual particles advected
in the HFR velocity field and released within the gulf for
the months of October 2013 (left panel) and February 2014 (right panel).
Black squares represent the locations of the four HFR antennas along the
Gulf of Manfredonia. Adapted from Sciascia et al. (2018).</p></caption>
            <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f15.png"/>

          </fig>

      <p id="d1e1692"><?xmltex \hack{\newpage}?>Moreover, the spatial distributions of time-averaged radar currents and
corresponding TKE (total kinetic energy), EKE (eddy kinetic energy), and the
absolute value of the products between temporal fluctuations of the
deviations from the time-averaged zonal and meridional velocity components
(ReS) have shown swirling areas for the first time at high spatiotemporal
resolution. The trapping zones, characterized by low values of TKE (see Fig. 16, top right panel), EKE and ReS at their cores, may help explain why this
channel is particularly rich in pelagic species, highlighting how
continuous high-resolution HFR-derived surface currents can improve
decision-making in fisheries resource management.</p>
</sec>
</sec>
</sec>
<sec id="Ch1.S3">
  <label>3</label><title>Discussion and preliminary assessment of the HFR regional capabilities</title>
      <p id="d1e1706">This initial review of scientific and societal applications using HFR data,
implemented in the Mediterranean coastal areas, has allowed us to know
their potential and limitations to continue contributing to the regional
observing system in addressing the existing regional environmental threats,
scientific key priorities and societal needs. Also considering the
current threats and the opportunities ahead along the UN Ocean Decade
(2021–2030), we have conducted a SWOT (i.e., strengths, weaknesses,
opportunities and threats) analysis, as schematized in Fig. 17.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F16" specific-use="star"><?xmltex \currentcnt{16}?><?xmltex \def\figurename{Figure}?><label>Figure 16</label><caption><p id="d1e1711">Map of the Malta–Sicily Channel showing the monthly averaged HFR
sea surface currents for January and June 2013 (top left and bottom left
panels, respectively) as well as the spatial distribution of the total kinetic energy (top
right panel) and the correlation coefficient between the first PC of both
HFR and Chl <inline-formula><mml:math id="M49" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> (bottom right panel). Original from Capodici et al. (2018),
graphical abstract.</p></caption>
        <?xmltex \igopts{width=312.980315pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f16.png"/>

      </fig>

      <p id="d1e1727">One of the main weaknesses found is the limited adoption of common data and
metadata models for HFR surface currents. As a result of international and
European efforts made in recent years towards HFR data harmonization and
distribution, as detailed in Lorente et al. (2022), the following have already been
defined: (i) the common data and metadata model for HFR surface currents
(Corgnati et al., 2018, 2019b; Mantovani et al., 2020), (ii) the tools for
near-real-time (Corgnati et al., 2020) and historical data processing
(Corgnati et al., 2019c),   (iii) the guidelines (Reyes et al., 2019) and (iv) training activities. Despite that, only 23 % of the near-real-time
and 15 % of the historical data from the Mediterranean HFR sites are
integrated into the European HFR node (Lorente et al., 2022), which was established in
November 2018 as a focal point for data management and distribution.</p>
      <p id="d1e1731">In the sphere of maritime safety, the main strength of HFRs is the provision
of high-spatiotemporal-resolution surface currents over wide coastal areas,
where most SAR incidents occur (see Sect. 2.1.1). HFRs are used as
alternatives to models for backtracking drifting objects in near-coastal
risk-prone environments and for complementing other scarce in situ observations,
also helping to assess and to improve ocean models through data
assimilation (see Sect. 2.1.2). In this regard, the provision of HFR data
uncertainties (Moore et al., 2019) might boost the use of HFR data for data
assimilation and model assessment. In addition to that, the machine-learning
approach whereby a neural network model is trained on past data and then used
to create short-term predictions (see Sect. 2.1.3) has gained ground in
recent years. The steady growth of the European HFR network (Rubio et
al., 2017; Roarty et al., 2019), increasing both the coastal coverage in
many countries and the length of the time series, will allow us to implement
these self-learning algorithms in other Mediterranean areas. Nevertheless,
there is a strong need for consensus on the methodology to generate these
scientific added-value products and on the definition and further adoption
of a common data and metadata model as well as quality control tests.
This lack of consensus hinders the operational distribution of standardized
HFR gap-filled data and derived STPs, which may lock the HFR data potential
for their use in several Lagrangian applications.</p>
      <p id="d1e1734">Additional efforts for unlocking interoperable HFR (basic or added value)
data access will greatly contribute to delivering greater uptake, use and value
from the HFR data. Once we are able to turn HFR data into customized
information, the further challenge is to extend the science-based
added-value products and applications to societally relevant downstream
services (Tintoré et al., 2019). To face this challenge, a clear
stakeholder engagement strategy is needed to identify, categorize and
analyze user needs and requirements. Through strengthened links with the
identified stakeholders, the HFR community will reinforce the user's
loyalty, whereas by involving them along the life cycle of the application
development will ensure the achievement of their needs, raising their
interest and usage. Furthermore, emerging HFR applications will enable new
communities and sectors to discover and use HFR data.</p>
      <p id="d1e1737">As a land-based remote sensing technology, HFRs are able to continuously
monitor the coastal ocean response to extreme events without the need to be
deployed at sea under severe met-ocean conditions, thus avoiding the risk faced by other observing platforms (i.e., research vessels, ferry boxes or
even autonomous instruments). Moreover, HFRs are also unaffected by cloud
coverage, which is usually associated with extreme storms and prevents
ocean color satellites and infrared radiometers from inferring and further
observing the Chl <inline-formula><mml:math id="M50" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> concentration and the SST, which are generally used
as proxies for surface circulation. In addition, it is worth highlighting
that under severe weather phenomena, near-real-time met-ocean information
gains value since it is essential to avoid risky situations and to support
emergency response at sea. The resilience of HFRs under unfavorable
weather conditions has allowed us to monitor and deeply investigate the
impacts of intense wind episodes, severe river freshwater discharges and
record-breaking storms as well as to observe the weakening or even the
reversal of main surface currents and jet streams (Sect. 2.2.1).
Furthermore, as it has been demonstrated that tsunami signature, irrespective of its
origin (i.e., seismic or atmospheric), can be clearly seen in HFR
radial currents, this opens up the possibility of using them as a useful
complement to other warning systems in places where those are either not
available or non-effective (Sect. 2.2.2). Nevertheless, despite the existing
risk from tsunamis and the frequent occurrence of meteotsunamis in
particular coastal areas of the Mediterranean Sea, no HFR tsunami alert system has been
installed in this region. Facing a growing
interest in these HFR new capabilities, several threats must be
addressed: (i) the installation of new systems to monitor the most probable
source areas and (ii) the extension of the range by using lower operational
frequencies in the Mediterranean Sea to be able to detect
tsunami-induced currents far offshore to offer early warning.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F17" specific-use="star"><?xmltex \currentcnt{17}?><?xmltex \def\figurename{Figure}?><label>Figure 17</label><caption><p id="d1e1749">SWOT analysis of the HFR capabilities and applications.
Dashed-line boxes around the text highlight those weaknesses, threats and
opportunities that have been addressed in the recommendations.</p></caption>
        <?xmltex \igopts{width=412.564961pt}?><graphic xlink:href="https://os.copernicus.org/articles/18/797/2022/os-18-797-2022-f17.png"/>

      </fig>

      <p id="d1e1758">The recognized capabilities of continuous HFR observations to analyze
the transport properties of the surface flow and to detect and track surface
eddies down to sub-mesoscale (Sect. 2.3.2) have allowed us (i) to
understand the phytoplankton distribution and to identify different local
retention scenarios (Sect. 2.3.1) as well as (ii) to investigate the role
played by the characteristic mesoscale variability and eddy generation in
the transport of biomass and pollutants as well as in the recruitment and abundance of
small pelagic species in the Mediterranean coastal waters (Sect. 2.3.3).
These practical applications have fostered the use of HFR data in supporting
coastal zone management (CZM) and assessing the variability in the
dynamics of marine ecosystems, becoming a valuable asset for contributing to
the achievement of Good Environmental Status (GES) of the Mediterranean
waters. However, it has been found that the number of detected eddies depends
on the HFR data availability, highlighting the need to combine HFR data
with numerical model outputs to bridge the spatiotemporal gap of the
observed data and to improve the reliability of the simulations. It should
also be noted that the limited coverage of HFR reduces the potential of
larger-scale applications and connectivity studies, thus requiring their
integration with other in situ and satellite observations as well as models, which
in turn will benefit from the future expansion of the HFR network.</p>
      <p id="d1e1762">Considering the key features of HFRs (see Sect. 1) as their main competitive
strengths when compared versus other observing platforms, it must be
recognized that the provision of information at the very near-surface layer
constitutes the most serious limitation, as highlighted in the SWOT analysis
from Lorente et al. (2022). In order to fully understand ocean dynamics,
knowledge of the 3D processes in the entire water column is essential as
well. A significant number of coastal ocean observatories in the
Mediterranean Sea (as described by Tintoré et al., 2019) encompass a
complex multi-platform network including HFRs, aiming to meet the primary
but challenging need to monitor both the surface and the water column. This
has motivated the development of techniques able to combine information
on the processes in the entire water column in order to provide a
three-dimensional picture of the overall dynamics. The combination of such
observations is challenging mainly for two reasons: the surface and ocean
interior are prone to different processes and forcings with different
spatiotemporal scales, and, at the same time, the capabilities to resolve
and characterize the diverse processes may be different for observing
platforms at the sea surface and in the water column. Despite the promising
results obtained by Berta et al. (2018) and Guihou et al. (2013) in the
Mediterranean Sea, necessary efforts must continue towards the further
development of methodologies to combine HFR data with water column
measurements and models.</p>
</sec>
<sec id="Ch1.S4">
  <label>4</label><title>Future prospects for HFR applications and recommendations</title>
      <p id="d1e1773">After the description of the current implementation status of HFR
applications in the Mediterranean coastal areas and based on the results
obtained from the previous SWOT analysis, we present  the prospects for
the future and a set of key recommendations. Future prospects for HFR
applications will benefit from the progressive implementation of the defined
recommendations: (i) to ensure that the potential of HFR data is fully
exploited in the development of operational monitoring systems at the
regional level; (ii) to help derive the added value achieved by the
European HFR network (Rubio et al., 2017, 2021; Corgnati et al., 2021; Lorente et al., 2022), such as data management centralization
and standard data distribution, the development of new products and
cross-disciplinary emerging applications, and the provision of training
workshops; and (iii) to include the recommendations in the long-term
monitoring strategy. This last point is crucial for (i) developing and
integrating the different COOSs into a robust regional ocean
observatory, (ii) ensuring that such integration is fully aligned with the
European and global roadmap, and (iii) addressing key science priorities
and societal challenges of the Mediterranean coastal regions.</p>
      <p id="d1e1776">Although the future prospects at the regional level are shared far beyond
the geographical borders of the Mediterranean Sea, recommendations have a
stronger regional focus: (i) to coordinate cross-national efforts (i.e.,
implementation of technical, financial and management approaches at national
and regional level, establishment of cross-border agreements for obtaining
dedicated frequency allocation for HFR technology), (ii) to account for
regional specificities (e.g., north–south unbalance in the monitoring
capabilities, prominent use of medium- and short-range HFR frequencies,
existence of ship noise and radio frequency interferences due to high marine
traffic density, high restrictions for obtaining the required HFR
installation licenses in coastal tourism areas) and to respond to
regional needs (in terms of scientific key priorities, societal needs and
existing environmental threats), and (iii) to map the existing and potential
HFR data regional end users, also facilitating the interaction with them. On
the basis of the future prospects, 12 recommendations can be highlighted in
the same alphabetical order as the weaknesses (items a–e) and threats (items
f–h) which are intended to be covered, as well as the opportunities (items
i–l) to be seized by each one of them (as in the schema in Fig. 17).</p>
      <p id="d1e1779"><list list-type="custom">
          <list-item><label>a.</label>

      <p id="d1e1784">Keep promoting the HFR data interoperability and distribution at the regional level. In order to reduce the bottlenecks that hinder HFR data
harmonization and their provision as open data, a data policy or data
sharing agreement between the parties providing and receiving data should be
defined and put in place. It might also partly resolve the difficulties of
sharing the HFR data held by companies or controlled by arrangements with
the private sector, who partially or fully funded the installations. The
collaboration with international initiatives will ensure convergence and
interoperability. The HFR data harmonization and sharing will ultimately
contribute to providing the research community with continuous and more
valuable coastal data and to underpinning the development of HFR
applications.</p>
          </list-item>
          <list-item><label>b.</label>

      <p id="d1e1790">Reinforce the Mediterranean's leadership for defining the
standard models of HFR basic and added-value products. Mediterranean
institutions are key players in the European and international HFR research
effort in multidisciplinary fields and in the development of applications,
as mostly covered in Sect. 2 of this work. In addition to that, HFR
experts from Mediterranean institutions are actively contributing to the
definition of the European HFR network roadmap detailed in Rubio et al. (2021), leading crucial tasks. One of these tasks aims to define the
standard model and to increase the availability and accuracy of the HFR wave
parameters, which are weaknesses included in Lorente et al. (2022).
Another important task focuses on seeking consensus on the methodology for
the provision of HFR added-value data products (i.e., gap-filling data).
The creation of partnerships between different research groups and
institutions in the context of European, regional and national projects
(Lorente et al., 2022) is contributing to moving forward both the expansion
of the HFR network and the main research areas, also fostering HFR data
interoperability and distribution, thereby helping to unlock HFR data potential,
discovery and usage.</p>
          </list-item>
          <list-item><label>c.</label>

      <p id="d1e1796">Enhance data discoverability, access and usability. The EuroGOOS
HFR Task Team has already taken the first steps towards the definition of
the user engagement strategy (Rubio et al., 2021) of building a database of
current and potential stakeholders with the input of some Mediterranean
institutions. However, stronger involvement is needed to avoid imbalances
between countries and greater efforts are required to move it forward by
means of programs that promote networking and coordination. Tight
interactions with stakeholders on a fit-for-purpose basis and the
enhancement of the societal impact of HFR data are major elements of the
strategy, especially towards ensuring long-term sustainability. Boosting
the regional involvement in this strategy will result in the spreading of
end-user applications at the regional and/or local level, also stimulating the
development of new ones in response to user feedback.</p>
          </list-item>
          <list-item><label>d.</label>

      <p id="d1e1802">Strengthen public–private partnerships (i) at the regional
level by enhancing inter-institutional collaboration to exchange
expertise, to build consortia and to share job opportunities in this
field. In this sense, the Mediterranean HFR network is benefitting from
the activities carried out in the context of the EuroGOOS HFR Task Team,
summarized in Rubio et al. (2021), and from ongoing regional joint
projects and existing national HFR coordination structures, as listed in
Lorente et al. (2022). It is also highly recommended to participate in
annual fora led by stakeholders, like the first MED-FORUM that brought
together the heads of maritime services or coast guards of almost all
Mediterranean states, aiming to develop a regional policy in the field of
maritime safety and to improve the efficiency of SAR services in the
Mediterranean area (Trevisanut et al., 2010). (ii) At the European level, partnerships could be strengthened by
being aligned with ongoing initiatives and projects, thereby contributing to the
EuroGOOS HFR Task Team and the main marine data portals (e.g., Copernicus
Marine Service, EMODnet, SeaDataNet), which will avoid duplication of
efforts. (iii) At the global level, this could be achieved by collaborating with international
institutions that are world leaders in HFR and ocean observation as well as
with the global HFR network to ensure consistency in data standards
and best practices. (iv) With the private sector, partnerships could be strengthened by transferring
knowledge and applications from academia to the operational
oceanography industry to turn them into commercial services, improving the
links between research and new technologies. The development of  existing
and potential applications will also assist HFR manufacturers in
marketing their technologies.</p>
          </list-item>
          <list-item><label>e.</label>

      <p id="d1e1808">Foster HFR data integration with other in situ and satellite data.
Exploiting the nature of their measurements, HFRs are currently being used
for filling the gaps in other sparse or lower-spatiotemporal-resolution
observations in coastal areas, as well as for improving and assessing
satellite observations. In this context, the
opportunity offered by the launch of the wide-swath Surface Water and Ocean
Topography (SWOT) altimeter expected in November 2022 should be considered. The SWOT
altimeter should be complemented with other remote and in situ sensors to fully
resolve the typical Mediterranean mesoscale structures of 10–100 km
(Gómez-Navarro et al., 2018). Additional complementarities might be
fostered with the monitoring of surface currents worldwide using
information from the Automatic Identification System (AIS) data streams
(Benaïchoucheet al., 2021), from which HFR measurements can be used as a
consistent ground-truth dataset for validation purposes and for increasing
the spatial resolution of the AIS-reconstructed fields at coastal areas. The
integration of HFR measurements with other multi-platform observations from
gliders or acoustic Doppler current profilers (ADCPs) (Manso-Narvarte et al., 2020) has already been implemented
and tested, particularly under the umbrella of the JERICO-NEXT project
(Griffa et al., 2019). This multi-platform combination underpins a sound
understanding of the three-dimensional coastal circulation, allowing the
broadening of HFR applications (i.e., below the surface). Data fusion and
integration will contribute to increasing the societal and scientific value
of all observations, not only the HFR ones.</p>
          </list-item>
          <list-item><label>f.</label>

      <p id="d1e1815">Boost HFR data assimilation for model improvement.
As shown in Sect. 2.1.2 of the present work, HFR surface current data
assimilation has been demonstrated to improve the model performance in many
studies (Paduan and Shulman, 2004; Barth et al., 2008;
Hernández-Lasheras et al., 2021). Furthermore,  HFR standard data
distribution in near-real time throughout the main European marine data
portals, facilitating data access and ensuring timeliness, makes them
ideal for efficient data assimilation in operational modeling
(Capet et al., 2020). However, WMOP is the only regional model from the
Mediterranean which systematically assimilates HFR data in its
operational chain (Hernández-Lasheras et al., 2021). As highlighted by
Capet et al. (2020), the lack of expertise, training and capacity building
is limiting the uptake of assimilation practices.</p>
          </list-item>
          <list-item><label>g.</label>

      <p id="d1e1821">Expand the pool of expertise by including not only HFR
technology, but also data management and applications, satellite remote sensing,
ocean modeling, data assimilation, training aspects, and exchanging and
sharing knowledge, tools, data and know-how between diverse research groups at
the European, regional and global levels.</p>
          </list-item>
          <list-item><label>h.</label>

      <p id="d1e1827">Train  the new generations of HFR technicians and scientists. They
are needed to ensure knowledge exchange and sufficient expertise to
allow for a significant expansion of the coverage and sustainability of
operations and HFR applications. This is currently being done in the
context of periodic workshops and summer schools (such as the recent ISSOR
and SICOMAR plus summer schools) within academia.
Moreover, the development of best practices for demonstrations is not only
key to reach satisfactory quality standards but also for fostering the
learning process. However, additional technical training courses provided by
manufacturers at the HFR operator level are recommended. Furthermore,
the participation of Mediterranean institutions and companies in the
creation of an international, intersectoral and interdisciplinary qualified
supporting training network will contribute to boosting knowledge and know-how
exchanges involving all actors (e.g., academia, operators, manufacturers,
private sector).</p>

      <p id="d1e1830">In addition to all abovementioned recommendations, seeking funding
is a compulsory task aiming to support, together with stakeholder
engagement and the training of new generations, the long-term
sustainability of the HFR network, data and applications at national,
regional and European levels. To this end, the EuroGOOS HFR Task Team has taken
early steps to prepare a competence matrix that will facilitate the building
of effective, interdisciplinary, intersectoral and well-balanced consortia,
grounded in shared research interests and goals, aiming to prepare
competitive bids and applications for funding, taking advantage of the
expertise of the team in diverse grant calls (Rubio et al., 2021). In
addition to research and grant funding, long-term infrastructure funding at
national, regional and European government level with financial input from
other operational users through regional consortia will be needed for a
truly sustainable infrastructure. For further details about the diverse
socioeconomic and technical challenges to be tackled during the
implementation of a sustained and integrated HFR regional network, the
reader is referred to Sect. 5.1 of the companion publication from
Lorente et al. (2022).</p>

      <p id="d1e1833">The Mediterranean HFR network must also take advantage of the opportunities
that arise in the framework of the UN Decade of Ocean Science for Sustainable
Development and the European Green Deal to lead the way towards future
prospects. The four recommendations given to benefit from the opportunities,
as included in the SWOT analysis (Fig. 17, bottom left panel), are as
follows.</p>
          </list-item>
          <list-item><label>i.</label>

      <p id="d1e1839">Expand the Mediterranean HFR network. Although this network
already represents 55 % of the HFR sites existing in the European
inventory (Lorente et al., 2022) and despite the very recent installations
(i.e., in the port  of Licata as well as in Portofino and Celle Ligure – Italy, in the port of
Menton and in Mimizan – France, and in Ta' Cenc in Gozo – Malta), with several new
deployments in an initial planning stage (i.e., in Haifa Bay – Israel,
Sardinia and Sicily islands, Gulf of Genoa, Gulf of Naples, Tuscany
Archipelago – Italy, Gulf of Trieste – Slovenia, and in the Aegean – Greece),
the Mediterranean coastal areas are still under-sampled. In this regard, it
should be noted that the spatiotemporal scales currently provided by the
HFRs in the Mediterranean allow us to monitor the current environmental
threats adequately but always in limited coastal areas, thus reducing the
potential of larger-scale applications (e.g., transport of organic matter
and pollutants, connectivity studies, data assimilation into models).
Therefore, aiming to improve the strategy of ocean observatories to
respond to regional needs for a better understanding of region-specific
processes towards a fit-for-purpose design, increased monitoring effort
by expanding and improving the HFR network is required, allowing for
coverage of a large geographical area on a routine basis. Accordingly, a
review of major scientific and social questions is needed including
environmental stressors and their impacts in the Mediterranean waters and
blue economy sectors to identify the benefit of the new deployments in
coordination with current monitoring actions (e.g., to identify gaps for
monitoring these risks, ensuring cost-effective observations).
To this end, cross-border coordination activities are key for the
involvement of other countries bordering the Mediterranean Sea along the
eastern and southern coastlines and to address issues related to frequency
sharing to avoid interference, as highlighted in Lorente et al. (2022).</p>
          </list-item>
          <list-item><label>j.</label>

      <p id="d1e1845">Further develop  emerging HFR applications in the
Mediterranean. The extension of the HFR surface current to fit multiple
purposes, aiming to address single to multiple environmental threats,
scientific questions and societal needs, requires a multidisciplinary
integrative approach and coordinated monitoring of different essential ocean
variables. In this context, it is worth mentioning that  HFR
multiparameter monitoring of the sea state allows the development of
diverse applications to tackle a wide range of coastal threats: (i) monitoring eutrophication in highly productive coastal waters, combining HFR
surface currents with thermistor chains, oxygen and turbidity sensors at
various depth increments, and addressing physical–biological interactions in
coastal basins (Cianelli et al., 2017; Hernández-Carrasco et al.,
2018a); (ii) monitoring the transport of floating marine litter and other
contaminants using surface current fields from HFRs and models (Declerck et
al., 2019); (iii) ship tracking (Dzvonkovskaya et al., 2007; Laws et
al., 2016); (iv) early tsunami and meteotsunami detection (Lipa et al., 2006;
Monserrat et al., 2006; Guèrin et al., 2008 ; Lipa et al., 2011, 2012; Gurgel et al., 2011, Dzvonkovskaya et al., 2012); (v) freshwater
monitoring (Meadows et al., 2013); (vi) extracting new information from
HFR signals, aiming to advance the understanding of key processes in
coastal areas, such as stratification (Shrira and Forget, 2015), air–sea
interaction (Berta et al., 2018) and mixing in the upper ocean, as well as near-surface
current shear; and (vii) promoting the HFR use for supporting marine
renewable energy resource assessment (i.e., winds, currents, waves) in the
coastal zone (Wyatt, 2012, 2021; Basáñez and
Pérez-Nuñunzuri, 2021; Mundaca-Moraga et al., 2021).
Additionally, since the intensity of the multiple stressors (e.g., climate-change effects, habitat loss and degradation, eutrophication, introduction
of alien species, fishing practices) is increasing throughout most of the
Mediterranean basin, trend analysis is an essential process in assessing the
state of the ocean of a region. This will contribute to effectively
informing current and future marine policies and management actions as well
as underpinning longer-term scientific objectives.</p>
          </list-item>
          <list-item><label>k.</label>

      <p id="d1e1851">Extend the Mediterranean HFR time series. This would enable
the widespread implementation of novel data science methodologies. It is
expected that the HFR measurements will be expanded in the next decade in both
space (i.e., new HFR systems) and time (i.e., longer time series). This
will increase the availability of multiyear surface current datasets, thus
contributing to boosting the application of HFR-derived STPs that use
self-learning algorithms to other Mediterranean locations. For such sites,
the stability of SOM solutions in time may be tested as well, or the
self-learning and training of SOM solutions might change in time to properly
reflect long-term changes in oceanographic conditions in a coastal area. The
further development of short-term predictive systems based upon HFR surface
current fields and their adaptation to the Mediterranean HFR network by
incorporating non-tidal components of currents will enhance STP
integration into operational maritime safety applications, which has
demonstrated their capacity to reduce the searching area (Roarty et al.,
2010).</p>
          </list-item>
          <list-item><label>l.</label>

      <p id="d1e1858">Regionally contribute to long-term major effort. Building a
sustained and fit-for-purpose European Ocean Observing System capable of
supporting the UN Decade of Ocean Science for Sustainable Development and the
European Green Deal should be twofold: (i) on the one hand, the
Mediterranean HFR network outcomes should be scientifically grounded to
further ensure the extension of science-based added-value products to
societally relevant downstream services (Tintoré et al., 2019). (ii) On the other hand, the Mediterranean HFR community's long-standing
cooperation must be further strengthened towards a co-designed and sustained
regional network, contributing to and, simultaneously, being benefited by the
European HFR Task Team (Corgnati et al., 2021; Rubio et al., 2021)
endorsement, roadmap and main achievements (as recommended by Lorente et
al., 2022).</p>
          </list-item>
        </list></p>
</sec>
<sec id="Ch1.S5" sec-type="conclusions">
  <label>5</label><title>Summary and conclusions</title>
      <p id="d1e1872">The socioeconomically vital and environmentally stressed coastal areas of
the Mediterranean Sea are some of the most exposed regions in the world due
to the impact of climate change, also being highly vulnerable target regions
for maritime safety, oil and marine litter pollution, fish stock
overexploitation, and met-ocean hazards. The high spatiotemporal variability
of the coastal dynamics requires the monitoring of these (sub-)mesoscale
processes at the right scale. HFRs are currently the only technology for
continuously monitoring surface currents (increasingly waves and winds) at
unprecedentedly high spatiotemporal resolution over coastal areas and with
relatively low cost and effort when compared with other traditional ocean
observing platforms. Their integration in ocean observing has boosted
progress in research on small-scale features and their interaction with
larger scales, also underpinning the further development of applications. In
this work, we present a review of the existing mature and emerging
scientific and societal applications using HFR data, developed to address
the major challenges identified in the Mediterranean coastal waters,
organized around three main topics: (i) maritime safety, (ii) extreme
hazards and (iii) environmental transport processes. In addition to previous
studies carried out at global and European scale on this topic, this
work also provides a list of strengths, weaknesses, opportunities and
threats of the existing HFR applications in the Mediterranean Sea. Finally,
we discuss the prospects for the future of HFR applications, and we
provide a set of recommendations aiming to maximize the contribution to
extending science-based HFR products to societally relevant downstream
services (Tintoré et al., 2019) to support blue growth in the
Mediterranean coastal areas, helping to meet the UN's Decade of Ocean
Science for Sustainable Development and EU's Green Deal goals.</p>
      <p id="d1e1875">Considering the steadily growing integration of HFRs in the COOSs of the
Mediterranean Sea and once their capabilities as an active and expanding
field of investigation has been demonstrated by a wide range of practical
applications, we can conclude that this consolidated land-based remote
sensing technology plays a key role in the development of fit-for-purpose
services for marine and maritime end users. However, major efforts
should still be made to unlock HFR interoperable data access and potential
as well as to further develop HFR scientific and societal
applications at the regional level, thus delivering greater uptake, use and
value. Fortunately, the opportunities provided in the framework of the UN
Decade of Ocean Science for Sustainable Development and the European Green
Deal can help to ensure the full exploitation of this HFR potential that
will contribute to further deepening our understanding of coastal ocean
dynamics and supporting sustainable blue growth in the Mediterranean Sea.
In this sense, collaboration at regional level is crucial to address
region-specific processes towards a fit-for-purpose and coordinated design
of monitoring actions, to identify the environmental threats and their
impacts on the environment and on blue sectors, to easily identify the
existing stakeholders, also fostering interaction with them, and to
engage potential users. This will help improve long-term
sustainability together with training activities for the next generations
and the search for funding. Certainly, this regional approach to strengthen
collaborations should always be aligned with global and European
strategies to ensure integration, benefiting from the European HFR
roadmap and the availability of near-real-time and long-term HFR
interoperable data that will boost research and underpin the further
development of HFR scientific and societal applications in the
Mediterranean coastal areas.</p>
      <p id="d1e1878">This paper constitutes the second part of a double contribution. Both
parts support each other in an integrative way and should be interpreted as
a single entity. The first part from Lorente et al. (2022) provides a
comprehensive overview of the current status, achievements, challenges,
coordinated efforts and roadmap to transform individual HFR systems into
a fully integrated HFR network in the Mediterranean. Additionally, this work
shows how these joint efforts have benefited and boosted HFR data
integration into services and the development of a broad range of
multidisciplinary science-based and fit-for-purpose applications,
contributing to leveraging the HFR data to their fullest potential.</p>
</sec>

      
      </body>
    <back><notes notes-type="codeavailability"><title>Code availability</title>

      <p id="d1e1885">The European HFR node shares the code to process native HFR data for quality control and to convert them to the standard format for distribution for the workflows of both near-real-time and reprocessed data, as defined in Corgnati et al. (2020, 2019), respectively.</p>
  </notes><notes notes-type="dataavailability"><title>Data availability</title>

      <p id="d1e1891">SOCIB HFR-Ibiza data, used in Sect. 2.1.1 (Fig. 2), Sect. 2.1.2
(Fig. 5) and Sect. 2.3.1 (Figs. 10 and 11), are available at
<uri>http://apps.socib.es/data-catalog/#/data-products/hf-radar-ibiza</uri> (Tintoré et al., 2020).
SOCIB drifter data, used in Sect. 2.1.1, are available at <uri>http://apps.socib.es/data-catalog/#/data-products/socib-exp-radar-sep2014</uri> (Tintoré et al., 2014) for
2014 (they have also been used in Sect. 2.1.2, Fig. 5), <uri>http://apps.socib.es/data-catalog/#/data-products/socib-int-radarapm-jul2016</uri> (Reyes et al., 2020c)
for 2016 and <uri>http://apps.socib.es/data-catalog/#/data-products/socib-enl-lagrangian-nov2018</uri> (Reyes et al., 2020b) for 2018. MIO's HFR-Toulon data is available <uri>http://hfradar.univ-tln.fr/HFRADAR/squel.php?content=accueil</uri> (last access: 5 May 2022, Dumas et al., 2022a) and real-time total currents (hourly data) in standard format are available for 2020 and 2021 in <uri>https://erddap.osupytheas.fr/erddap/files/cmems_nc_cf0e_c84a_8ead/</uri> (last access: 5 May 2022, Dumas et al., 2022b)</p>
  </notes><app-group>
        <supplementary-material position="anchor"><p id="d1e1913">The supplement related to this article is available online at: <inline-supplementary-material xlink:href="https://doi.org/10.5194/os-18-797-2022-supplement" xlink:title="zip">https://doi.org/10.5194/os-18-797-2022-supplement</inline-supplementary-material>.</p></supplementary-material>
        </app-group><notes notes-type="authorcontribution"><title>Author contributions</title>

      <p id="d1e1922">ER and PL conceived the idea of this paper and fostered the
collaboration as MONGOOS HFR Task Team co-chairs, being in charge of overall
direction and planning. All authors contributed to the writing of the
different sections of the paper, as follows.
ER took the lead in writing the Abstract and Sects. 1, 3, 4 and 5, also
contributing to Sect. 2.1. Other authors contributed to
Sect. 1 (CAG, DD, MB, SS) and Sect. 4 (YT, MB, RG). MB also contributed to
the summary of HFR capabilities in Sects. 3 and 5.
CRS, VC, ML, HM, AD, AG, AM, AR and ER (designed Fig. 1) collected the
information from the maritime safety and rescue agencies for their
respective countries.
CRS and ML (designed Fig. 3) contributed to the introduction of
Sect. 2.1, and, together with VC, AR (designed Fig. 2), JT and ER, they
shaped Sect. 2.1.1.
PL (designed Fig. 4), BM, JHL (designed Fig. 5), EA and ER wrote
Sect. 2.1.2.
IHC, AO, HM (designed Fig. 6), IV and VD took the lead in writing  Sect. 2.1.3.
MB (designed Fig. 7), AG, LC and CM contributed to the data analysis and text
drafting in Sect. 2.2.1, in particular for the case study in the Ligurian
Sea. In this section, PL (designed Fig. 8) and ER addressed two case
studies in the Ebro Delta and one in the Strait of Gibraltar.
CAG took the lead in writing Sect. 2.2.2, to which BM, ML and MJF also
contributed.
AM, ACE, IHC (designed Figs. 10 and 11) and AO contributed to the writing of
Sect. 2.3.1.
MBen – Consorzio LaMMA (designed Figs. 12 and  13), CB, ST, BD, MU,
MJF, PF, EZ, HM and IV wrote Sect. 2.3.2.
MM, DC (designed Fig. 14), RS (designed Fig. 15), FC (designed
Fig. 16), CAG, MB, AG, IH and AO contributed to Sect. 2.3.3. Particularly,
RS and MM focused on the Gulf of Manfredonia, DC on the Gulf of Naples, and
FC on the Malta–Sicily case studies.
AM, IV, CAG, JT and the MONGOOS co-chairs, VC and AO, provided critical
feedback and helped shape the final version of the paper during the
internal review process.
All authors have read and agreed to the submission of the paper for
publication.</p>
  </notes><notes notes-type="competinginterests"><title>Competing interests</title>

      <p id="d1e1928">Authors Maria Fattorini, Roberto Gómez and Pablo Lorente are currently employed at Qualitas Instruments Lda, at Helzel Messtechnik GmbH and at NOLOGIN Consulting SL, respectively. However, the authors have not advertised commercial products, and the research has not been sponsored by any one of the companies.
At least one of the authors is a guest member of the editorial board of the special issue of <italic>Ocean Science</italic>. The peer-review process was guided by an independent editor, and the authors also have no other competing interests to declare.</p>
  </notes><notes notes-type="disclaimer"><title>Disclaimer</title>

      <p id="d1e1937">Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.</p>
  </notes><notes notes-type="sistatement"><title>Special issue statement</title>

      <p id="d1e1943">This article is part of the special issue “Advances in interdisciplinary studies at multiple scales in the Mediterranean Sea”. It is a result of the 8th MONGOOS Meeting &amp; Workshop, Trieste, Italy, 3–5 December 2019.</p>
  </notes><ack><title>Acknowledgements</title><p id="d1e1949">This work has been possible thanks to the MONGOOS (Mediterranean Operational Network for the Global Ocean Observing System) collaborative network, aimed toward
long-term synergies between multidisciplinary working groups in the Mediterranean Sea in order to launch strategic initiatives and pursue funding for innovative research projects. Pierpaolo Falco and Enrico Zambianchi acknowledge partial funding from the Italian Ministry for University and Research through the 2017 PRIN project “Exploring the fate of Mediterranean microplastics: from distribution pathways to biological effects” (EMME, grant agreement no. 2017WERYZP). We are furthermore grateful for the valuable information about  maritime rescue activity for 2019 provided by the Spanish Maritime Search and Rescue Agency, the Italian coast guard, the French CROSSMED, the Ministry of Maritime Affairs, Transport and Infrastructure from Croatia, and the search and rescue coordination centers from the SRRs (search and rescue regions) of Slovenia and Malta. We also acknowledge the Spanish Meteorological Agency AEMET for providing HARMONIE atmospheric fields and the European High-Frequency Radar Node (EU HFR NODE) for providing high-frequency radar surface current data from European and US radial sites at <uri>https://thredds.hfrnode.eu.html</uri> (last access: 5 May 2022). SOCIB's WMOP simulations are available upon request to info@socib.es and can be viewed at <uri>https://www.socib.es/?seccion=modelling&amp;facility=forecast</uri> (last access: 16 May 2022). HFR-LaMMA data, used in Sect. 2.3.2, can be viewed at <uri>http://www.lamma.rete.toscana.it/meteo/osservazioni-e-dati/radar-hf</uri>, and HFR-NAdr data, used in Sect. 2.1.1. (Fig. 3), can be viewed at <ext-link xlink:href="http://www.nib.si/mbp/en/oceanographic-data-and-measurements/other-oceanographic-data/hf-radar-2">http://www.nib.si/mbp/en/oceanographic-data-and-measurements/</ext-link>. Data from the International Maritime Organization, mentioned in Sect. 1, are available from the Flow Monitoring Displacement Tracking Matrix website: <uri>https://migration.iom.int/europe?type=arrivals</uri> (last access: 16 May 2022).
Eurostat statistics for maritime transport of goods, mentioned in the Introduction, are available at <ext-link xlink:href="https://ec.europa.eu/eurostat/statistics-explained/index.php?title=Maritime_transport_of_goods_-_quarterly_data&amp;oldid=485429#EU_ports:_activity">https://ec.europa.eu/eurostat/</ext-link> (last access: 16 May 2022).
The “Sub-regional Mediterranean Sea Indicators” tool, mentioned in the Sect. 1, is available at the following website:   <uri>https://apps.socib.es/subregmed-indicators/</uri> (last access: 16 May 2022).
The SAR incidences in France, included in Sect. 2.1.1, were obtained from the website of the French Ministry of the Sea: <uri>https://www.mer.gouv.fr/surveillance-et-sauvetage-en-mer</uri> (last access: 16 May 2022).</p><p id="d1e1976">The authors would like to thank Stephan Grilli from the University of Rhode Island (USA) for the design of Fig. 9 (from Sect. 2.2.2) and Leonardo Bagaglini for processing the data shown in Fig. 12 (from Sect. 2.3.2). Finally, the authors would like to express their gratitude to the internal reviewers, Anne Molcard, Ivica Vilibic, Charles-Antoine Guèrin and Joaquín Tintoré, as well as to the MONGOOS co-chairs, Vanessa Cardin and Alejandro Orfila, for their careful and meticulous reading of the paper. Their detailed and comprehensive reviews have been very helpful to improve the structure and reading as well as to finalize the paper.</p></ack><notes notes-type="financialsupport"><title>Financial support</title>

      <p id="d1e1981">Publication fees are provided by EuroSea (EU Horizon 2020 research and innovation program, grant agreement ID no. 862626) and JERICO-S3 (EU Horizon 2020 research and innovation program, grant agreement ID no. 871153). Research was supported by the following projects: CMEMS-INSTAC phase II, which provides the context of the activities for HFR data harmonization, standardization and distribution; the IBISAR CMEMS User-Uptake project (67-UU-DO-CMEMS-DEM4_LOT7); MEDCLIC project (LCF/PR/PR14/11090002, supported by La Caixa Foundation) that contributed to the development of the WMOP model; the CARTHE III project (Prime Award no. SA 18-14, subcontract agreement SPC-000649) and CALYPSO Departmental Research Initiative (grant no. N00014-18-1-2782), which supported the development of the methodology for extreme event monitoring in the Ligurian Sea (Sect. 2.2.1); the IMPACT project (EU funded, PC Interreg VA IFM 2014–2020, Prot. ISMAR no. 0002269) that funded the HFR network in the Ligurian Sea; the JERICO-NEXT project (EU Horizon 2020, grant agreement no. 654410) under which the assimilation of HFR data in WMOP (Sect. 2.1.2) and the biological connectivity application in the Gulf of Manfredonia (Sect. 2.3.3) have been developed; the COCONET project (EU FP7, grant agreement no. 287844) and the Italian national projects SSDPESCA and RITMARE; and the SICOMAR-PLUS EU Interreg Marittimo project, which funded the recent upgrades to the HFR installations of the MIO in Toulon.</p>
  </notes><notes notes-type="reviewstatement"><title>Review statement</title>

      <p id="d1e1988">This paper was edited by Anna Rubio and reviewed by two anonymous referees.</p>
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