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  <front>
    <journal-meta>
      <journal-id journal-id-type="publisher-id">Ecological Safety of Coastal and Shelf Zones of Sea</journal-id>
      <journal-title-group>
        <journal-title xml:lang="en">Ecological Safety of Coastal and Shelf Zones of Sea</journal-title>
        <trans-title-group xml:lang="ru">
          <trans-title>Экологическая безопасность прибрежной и шельфовой зон моря</trans-title>
        </trans-title-group>
      </journal-title-group>
      <issn publication-format="print">2413-5577</issn>
    </journal-meta>
    <article-meta>
      <article-id pub-id-type="publisher-id">20260307</article-id>
      <article-id pub-id-type="edn">BCBKRB</article-id>
      <article-categories>
        <subj-group subj-group-type="toc-heading" xml:lang="ru">
          <subject>Научная статья</subject>
        </subj-group>
        <subj-group subj-group-type="article-type">
          <subject>Research Article</subject>
        </subj-group>
      </article-categories>
      <title-group>
        <article-title xml:lang="en">Distribution of Macrophytobenthos in the Landscapes of the Natural Monument “Coastal Aquatic Complex at Cape Sarych”</article-title>
        <trans-title-group xml:lang="ru">
          <trans-title>Распределение макрофитобентоса в ландшафтах памятника природы «Прибрежный аквальный комплекс у мыса Сарыч»</trans-title>
        </trans-title-group>
      </title-group>
      <contrib-group>
        <contrib contrib-type="author">
          <name-alternatives>
            <name xml:lang="en">
              <surname>Mironova</surname>
              <given-names>N. V.</given-names>
            </name>
            <name xml:lang="ru">
              <surname>Миронова</surname>
              <given-names>Н. В.</given-names>
            </name>
          </name-alternatives>
          <contrib-id contrib-id-type="orcid">0000-0001-7110-7081</contrib-id>
          <contrib-id contrib-id-type="researcher-id">AAC-9421-2022</contrib-id>
          <contrib-id contrib-id-type="scopus-author-id">9889-3824</contrib-id>
          <email>dr.nataliya.mironova@yandex.ru</email>
          <xref ref-type="aff" rid="aff1"/>
        </contrib>
        <contrib contrib-type="author">
          <name-alternatives>
            <name xml:lang="en">
              <surname>Pankeeva</surname>
              <given-names>T. V.</given-names>
            </name>
            <name xml:lang="ru">
              <surname>Панкеева</surname>
              <given-names>Т. В.</given-names>
            </name>
          </name-alternatives>
          <contrib-id contrib-id-type="orcid">0000-0002-8933-6103</contrib-id>
          <contrib-id contrib-id-type="researcher-id">FAA-2365-2022</contrib-id>
          <contrib-id contrib-id-type="scopus-author-id">4920-0290</contrib-id>
          <email>tatyanapankeeva@yandex.ru</email>
          <xref ref-type="aff" rid="aff1"/>
        </contrib>
      </contrib-group>
      <aff-alternatives id="aff1">
        <aff xml:lang="en">
          <institution>A. O. Kovalevsky Institute of Biology of the Southern Seas of RAS</institution>
          <addr-line>Sevastopol</addr-line>
          <country>Russia</country>
        </aff>
        <aff xml:lang="ru">
          <institution>ФГБУН ФИЦ «Институт биологии южных морей имени А.О. Ковалевского РАН»</institution>
          <addr-line>Севастополь</addr-line>
          <country>Россия</country>
        </aff>
      </aff-alternatives>
      <pub-date date-type="pub" iso-8601-date="2026-09-30" publication-format="electronic">
        <day>30</day>
        <month>09</month>
        <year>2026</year>
      </pub-date>
      <issue>3</issue>
      <fpage>110</fpage>
      <lpage>124</lpage>
      <history>
        <date date-type="received" iso-8601-date="2026-02-09">
          <day>09</day>
          <month>02</month>
          <year>2026</year>
        </date>
        <date date-type="rev-recd" iso-8601-date="2026-03-17">
          <day>17</day>
          <month>03</month>
          <year>2026</year>
        </date>
        <date date-type="accepted" iso-8601-date="2026-06-30">
          <day>30</day>
          <month>06</month>
          <year>2026</year>
        </date>
      </history>
      <permissions>
        <copyright-statement xml:lang="en">Copyright © 2026, Mironova N.V., Pankeeva T.V.</copyright-statement>
        <copyright-statement xml:lang="ru">Copyright © 2026, Миронова Н.В., Панкеева Т.В.</copyright-statement>
        <copyright-year>2026</copyright-year>
        <copyright-holder xml:lang="en">Mironova N.V., Pankeeva T.V.</copyright-holder>
        <copyright-holder xml:lang="ru">Миронова Н.В., Панкеева Т.В.</copyright-holder>
        <ali:free_to_read xmlns:ali="http://www.niso.org/schemas/ali/1.0/"/>
        <license>
          <ali:license_ref xmlns:ali="http://www.niso.org/schemas/ali/1.0/">https://creativecommons.org/licenses/by-nc/4.0/</ali:license_ref>
        </license>
      </permissions>
      <self-uri xlink:href="https://ecological-safety.ru/repository/issues/2026/03/07/" xlink:title="Страница статьи">https://ecological-safety.ru/repository/issues/2026/03/07/</self-uri>
      <abstract xml:lang="en">
        <p>For the first time, based on a landscape approach, the features of the spatial distribution of benthic vegetation, floristic composition, and qualitative and quantitative characteristics of the macrophyto-benthos of the regional natural monument “Coastal Aquatic Complex at Cape Sarych” (Southern Coast of Crimea, Sevastopol region) are shown. The study used materials from hydrobotanical and landscape surveys conducted in this area in the summer of 2021. A landscape map of the water area was compiled, and seven underwater landscapes were identified, featuring the key macrophyte species Ericaria crinita, Gongolaria barbata and Phyllophora crispa. For each landscape contour, the total macrophyte biomass (TMB) and the proportion of key macrophyto-benthic species were calculated. The comparative analysis showed that the landscape of the shallow zone (0.5–1 m) has the greatest variability in TMB values (2036.5 ± 264.6)–(8167.6 ± 465.7) g·m⁻² raw mass and proportions of E. crinita, G. barbata (4–83%). The contribution of epiphytes does not exceed 3–21% TMB. Maximum values of TMB (6972.8 ± 371.2)–(10 673.3 ± 654.8) g·m⁻² raw mass and high contribution of E. crinita, G. barbata (53–77%) were observed in the landscapes upper shoreface (1–5 m), where the highest proportion of epiphytic algae was also recorded (23–34%). The TMB in landscapes of the gently (5–15 m) dipping accumulation plain was characterized by relatively low values, which varied slightly (1312.7 ± 141.3)–(2463.0 ± 196.7) g·m⁻² raw mass, with the contribution of P. crispa increasing sharply with depth (from 20 to 87%), whereas that of E. crinita and G. barbata significantly decreasing (from 66 to 2%); the proportion of epiphytic plants was 8–23%. It was established that the marine flora contained a significant number of algal species listed in Red Data Books, which confirms the conservation value of the studied aquatic area. However, species of macrophytes, indirectly indicating pollution of the protected water area, were found in the algoflora of the nature monument. In the coastal zone under recreational pressure, a mass development of green algae (Ulva rigida, Ulva intestinalis, Cladophora laetevirens) was observed, along with the highest proportion of polysaprobic and the maximum contribution of annual and summer macrophyte species inhabiting waters with an elevated organic content. The obtained results can be utilized for optimizing the conservation regime of the natural monument.</p>
      </abstract>
      <trans-abstract xml:lang="ru">
        <p>Впервые на основе ландшафтного подхода оцениваются флористический состав, качественные и количественные характеристики макрофитобентоса и особенности его распределения в акватории памятника природы регионального значения «Прибрежный аквальный комплекс у мыса Cарыч» (Южный берег Крыма, район г. Севастополя). Использованы материалы гидроботанической и ландшафтной съемок, проведенных в этом районе летом 2021 г. Составлена ландшафтная карта акватории, выделено семь подводных ландшафтов с участием ключевых видов макрофитов Ericaria crinita, Gongolaria barbata и Phyllophora crispa. Для каждого ландшафтного контура рассчитаны общая биомасса макрофитов и доля ключевых видов макрофитобентоса. Сравнительный анализ показал, что ландшафты мелководной зоны (глубина 0.5–1 м) отличаются наибольшей вариабельностью общей биомассы макрофитов – (2036.5 ± 264.6)–(8167.6 ± 465.7) г·м⁻² сырой массы – и доли E. crinita, G. barbata (4–83 %). Вклад эпифитов не превышает 3–21 % общей биомассы макрофитов. Максимальные значения общей биомассы макрофитов – (6972.8 ± 371.2)–(10 673.3 ± 654.8) г·м⁻² сырой массы – и высокий вклад E. crinita, G. barbata (53–77 %) отмечены в ландшафтах, относящихся к подводному склону (глубина 1–5 м), где также зарегистрирована наибольшая доля эпифитных водорослей (23–34 %). Показатели общей биомассы макрофитов в ландшафтах слабонаклонной равнины (глубина 5–15 м) относительно невысоки и слабо варьируют – от (1312.7 ± 141.3) до (2463.0 ± 196.7) г·м⁻² сырой массы; при этом вклад P. crispa резко возрастает с глубиной (с 20 до 87 %), а доля E. crinita и G. barbata существенно снижается (с 66 до 2 %), доля эпифитной синузии составляет 8–23 %. В составе морской флоры зарегистрировано значительное количество видов водорослей, занесенных в Красные книги, что подтверждает высокую природоохранную ценность изучаемой акватории. Однако в альгофлоре памятника природы обнаружены виды макрофитов, которые косвенно указывают на загрязнение охраняемой акватории. В прибрежной зоне, испытывающей рекреационную нагрузку, отмечено массовое развитие зеленых водорослей (Ulva rigida, U. intestinalis, Cladophora laetevirens), наибольшая доля полисапробионтов и максимальный вклад однолетних и сезонно-летних видов макрофитов, обитающих в воде с повышенным уровнем антропогенной эвтрофикации. Полученные результаты могут быть использованы для оптимизации природоохранного режима памятника природы.</p>
      </trans-abstract>
      <kwd-group xml:lang="en">
        <kwd>bottom vegetation</kwd>
        <kwd>Ericaria crinita</kwd>
        <kwd>Gongolaria barbata</kwd>
        <kwd>Phyllophora crispa</kwd>
        <kwd>specially protected natural areas</kwd>
        <kwd>landscape structure</kwd>
        <kwd>Black Sea</kwd>
        <kwd>Sevastopol</kwd>
      </kwd-group>
      <kwd-group xml:lang="ru">
        <kwd>донная растительность</kwd>
        <kwd>Ericaria crinita</kwd>
        <kwd>Gongolaria barbata</kwd>
        <kwd>Phyllophora crispa</kwd>
        <kwd>особо охраняемые природные территории</kwd>
        <kwd>ландшафтная структура</kwd>
        <kwd>Черное море</kwd>
        <kwd>Севастополь</kwd>
      </kwd-group>
      <funding-group>
        <funding-statement xml:lang="en">This work was carried out within the framework of IBSS state research assignment “Comprehensive study of the functioning mechanisms of marine biotechnological complexes with the aim of obtaining bioactive substances from hydrobionts” (No. 124022400152-1).</funding-statement>
        <funding-statement xml:lang="ru">Работа выполнена в рамках государственного задания ФИЦ ИнБЮМ по теме «Комплексное исследование механизмов функционирования морских биотехнологических комплексов с целью получения биологически активных веществ из гидробионтов» (№ гос. регистрации 124022400152-1).</funding-statement>
      </funding-group>
    </article-meta>
  </front>
  <body>
    <p>Текст статьи не включен.</p>
  </body>
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