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<article xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:ali="http://www.niso.org/schemas/ali/1.0/" dtd-version="1.4" article-type="research-article" xml:lang="en"><front><journal-meta><journal-title-group><journal-title xml:lang="ru">Теоретическая и прикладная экология</journal-title></journal-title-group><issn publication-format="print">1995-4301</issn><issn publication-format="electronic">2618-8406</issn></journal-meta><article-meta><article-id pub-id-type="doi">10.25750/1995-4301-2026-1-161-168</article-id><article-categories><subj-group><subject>Other</subject></subj-group></article-categories><title-group><article-title xml:lang="ru">Распространение солеустойчивой растительности в поймах при техногенном засолении почв</article-title><trans-title-group xml:lang="en"><trans-title>Salt-tolerant plant distribution within floodplain ecosystems due to technogenic soil salinization</trans-title></trans-title-group></title-group><contrib-group><contrib contrib-type="author"><name-alternatives><name xml:lang="ru"><surname>Еремченко</surname><given-names>О. З.</given-names></name><name xml:lang="en"><surname>Eremchenko</surname><given-names>O. Z.</given-names></name></name-alternatives><xref ref-type="aff" rid="aff1"/><xref ref-type="aff" rid="aff2"/><email>eremch@psu.ru</email><contrib-id contrib-id-type="orcid">https://orcid.org/0000-0003-3581-0874</contrib-id></contrib><contrib contrib-type="author"><name-alternatives><name xml:lang="ru"><surname>Малышкина</surname><given-names>Е. Е.</given-names></name><name xml:lang="en"><surname>Malyshkina</surname><given-names>E. E.</given-names></name></name-alternatives><xref ref-type="aff" rid="aff1"/><xref ref-type="aff" rid="aff2"/><contrib-id contrib-id-type="orcid">https://orcid.org/0000-0002-7251-7637</contrib-id></contrib><contrib contrib-type="author"><name-alternatives><name xml:lang="ru"><surname>Пахоруков</surname><given-names>И. В.</given-names></name><name xml:lang="en"><surname>Pakhorukov</surname><given-names>I. V.</given-names></name></name-alternatives><xref ref-type="aff" rid="aff1"/><xref ref-type="aff" rid="aff2"/><contrib-id contrib-id-type="orcid">https://orcid.org/0000-0001-8152-0283</contrib-id></contrib><aff-alternatives id="aff1"><aff><institution xml:lang="en">Perm State National Research University (Perm, Russia)</institution></aff></aff-alternatives><aff-alternatives id="aff2"><aff><institution xml:lang="ru">Пермский государственный национальный исследовательский университет (Пермь, Россия)</institution></aff></aff-alternatives></contrib-group><pub-date pub-type="epub" iso-8601-date="2026-03-25"><day>25</day><month>03</month><year>2026</year></pub-date><issue>1</issue><fpage>161</fpage><lpage>168</lpage><self-uri xlink:href="http://www.envjournal.ru/ari/v2026/v1/26117.pdf" xlink:title="http://www.envjournal.ru/ari/v2026/v1/26117.pdf">http://www.envjournal.ru/ari/v2026/v1/26117.pdf</self-uri><self-uri content-type="pdf" xlink:href="publication-46eac1ce-e40d-4272-a7d3-7b743105d11c.pdf" xlink:title="PDF"/><abstract xml:lang="ru"><p>На основе маршрутных исследований было показано, что в составе изреженной астительности пойм двух малых рек (Чёрная и Лёнва), расположенных в зонах воздействия отходов калийного производства (Пермский край), доминировали рудеральные однолетние и многолетние травянистые виды, присутствовали факультативные и облигатные Spergularia salina J. et C. Presl, Triglochin maritimum L.) галофиты. На двух участках с солеустойчивой растительностью изучили почвенно-экологические условия произрастания. Почвенные пробы отбирали летом 2022 г. в четыре периода наблюдений в десятикратной повторности. В полевых условиях измеряли pH и Eh корнеобитаемого слоя почвы (0–10 см); в почвенных пастах при влажности 50 % определяли активность Na+, K+, Cl–. В пойме р. Чёрной поверхностный слой почвы характеризовался нейтральной и слабощелочной реакцией среды (pH 7,3–8,4) и слабо восстановительными условиями (Eh 139–282 мВ), засоление отсутствовало (по уровню активности Na+). В верхнем слое почвы поймы р. Лёнвы отмечалась значительная вариабельность pH (от 5,4 до 6,9); Eh колебалась от восстановительных (–135 мВ) до окислительных значений (468 мВ). В почве проявлялось засоление разной степени (от слабой до сильной), в ряде случаев засоление отсутствовало. Активность К+ в почве достигала уровня активности Na+, активность Cl– превышала суммарную активность засоляющих катионов. Изреженную растительность пойм оконтуривали с использованием летних спутниковых снимков в комбинации «Естественные цвета». За период с 2015 по 2021 гг. площадь, занятая солеустойчивой растительностью, в пойме р. Чёрной увеличилась в 1,8 раза и составила 8,7 га, а в пойме р. Лёнвы – в 1,6 раза и достигла 22,2 га.</p></abstract><abstract xml:lang="en" abstract-type="summary"><p>According to site research, the vegetation that grows in the floodplain ecosystems of the Chyornaya and Lyonva rivers, located in areas affected by potash production waste, is dominated by ruderal annual and perennial herbaceous species. Additionally, obligate (Spergularia salina J. et C. Presl, Triglochin maritimum L.) and facultative halophytes were found. The pedological and ecological factors affecting the growth were analyzed in two distinct areas with salt-tolerant vegetation. The samples were collected ten times during the summer 2022 across four distinct observational intervals. The pH levels and redox potential within the root zone (0–10 cm) were field-measured. Na+, K+, and Cl- content were determined in soil at humidity of 50 %. In the Chernaya River floodplain, the topsoil exhibited a neutral to slightly alkaline pH (7.3–8.4) and weakly reducing conditions (139–282 mV). Salinization was notably absent, as indicated by the measured levels of Na+ activity. In the topsoil of the Lyonva River floodplain, the pH levels varied from 5.4 to 6.9. Moreover Eh varied from reducing (as low as –135 mV) to oxidizing values (468 mV). The soil exhibited both varying degrees of salinization (from mild to severe) as well as its absence. The K+ activity in the soil reached that of Na+, while the Cl– activity exceeded the total activity of the salinizing cations. Through the use of true color satellite imagery obtained during the summer months, it was possible to identify the sparse flora distribution within the floodplain ecosystems. Between 2015 and 2021, the expanse of salt-tolerant vegetation within the Chyornaya River floodplain grew by 1.8 times, totaling 8.7 hectares, and in the Lyonva River floodplain it increased by 1.6 times, reaching 22.2 hectares.</p></abstract><kwd-group xml:lang="ru"><kwd>синантропизация</kwd><kwd>калийная промышленность</kwd><kwd>солеустойчивая растительность</kwd><kwd>техногенное засоление</kwd><kwd>спутниковое картографирование</kwd></kwd-group><kwd-group xml:lang="en"><kwd>synanthropization</kwd><kwd>potash industry</kwd><kwd>salt-tolerant plants</kwd><kwd>technogenic secondary salinization</kwd><kwd>satellite-based mapping</kwd></kwd-group><funding-group><funding-statement xml:lang="ru">Исследование выполнено за счёт гранта Российского научного фонда (проект № 24-27-00324).</funding-statement></funding-group></article-meta></front><back><ref-list><ref id="ref1"><mixed-citation publication-type="other" xml:lang="ru">1. Enríquez-de-Salamanca Á. 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