Preprints
https://doi.org/10.5194/egusphere-2026-4131
https://doi.org/10.5194/egusphere-2026-4131
22 Jul 2026
 | 22 Jul 2026
Status: this preprint is open for discussion and under review for Biogeosciences (BG).

Late Holocene evolution of a dystrophic Tatra Lake: natural trophic changes revealed by multi-proxy data

Elwira Sienkiewicz, Karolina Kaucha, Michał Gąsiorowski, Urszula Kowalewska, and Michał Słowiński

Abstract. Dystrophic lakes, characterized by dark-colored water, low transparency, and low pH, are relatively common in the mountainous and lowland regions of temperate and boreal zones. The occurrence of dystrophic conditions depends on hydrological, climatic, and biological factors, including surface and groundwater inflows and outflows, precipitation, air temperature, and vegetation within the lake's catchment. A change in any of these factors can lead to either an increase or a decrease in the degree of lake dystrophy. In this study, we present changes in the trophic status of a small forest lake located in the lower part of the Tatra Mountains (1,089 m a.s.l.; Western Carpathians, Poland). The lake is located within the Tatra National Park, and its natural dystrophic character is one of the features protected under the park's conservation objectives. We aimed to determine whether these dystrophic conditions are of natural origin and have persisted over a long period. To investigate this, we analysed a 1.4-m sediment core spanning the last 3,150 years using a range of geochemical and paleobiological methods, including elemental analysis, stable carbon and nitrogen isotope analyses, and analyses of diatom and Cladocera assemblages. Changes in the species composition of diatoms and Cladocera indicate that dystrophic conditions did not persist throughout the entire study period. The lake was dominated by species characteristic of meso-oligotrophic and oligotrophic water bodies, with only a brief period during which species indicative of dystrophic conditions appeared, coinciding with a low-water phase around 2700–2350 cal. yr BP. Permanent dystrophic conditions became established no earlier than approximately 950 cal. yr BP, which is relatively late compared with many lowland lakes.

Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims made in the text, published maps, institutional affiliations, or any other geographical representation in this paper. While Copernicus Publications makes every effort to include appropriate place names, the final responsibility lies with the authors. Views expressed in the text are those of the authors and do not necessarily reflect the views of the publisher.
Share
Elwira Sienkiewicz, Karolina Kaucha, Michał Gąsiorowski, Urszula Kowalewska, and Michał Słowiński

Status: open (until 08 Sep 2026)

Comment types: AC – author | RC – referee | CC – community | EC – editor | CEC – chief editor | : Report abuse
Elwira Sienkiewicz, Karolina Kaucha, Michał Gąsiorowski, Urszula Kowalewska, and Michał Słowiński
Elwira Sienkiewicz, Karolina Kaucha, Michał Gąsiorowski, Urszula Kowalewska, and Michał Słowiński

Viewed

Total article views: 138 (including HTML, PDF, and XML)
HTML PDF XML Total BibTeX EndNote
101 20 17 138 22 21
  • HTML: 101
  • PDF: 20
  • XML: 17
  • Total: 138
  • BibTeX: 22
  • EndNote: 21
Views and downloads (calculated since 22 Jul 2026)
Cumulative views and downloads (calculated since 22 Jul 2026)

Viewed (geographical distribution)

Total article views: 124 (including HTML, PDF, and XML) Thereof 124 with geography defined and 0 with unknown origin.
Country # Views %
  • 1
1
 
 
 
 
Latest update: 14 Aug 2026
Download
Short summary
Combined diatom, Cladocera and geochemical records show that TSN did not follow a typical eutrophication pathway. Instead, it evolved from oligo-mesotrophic to oligotrophic and finally to persistent dystrophic conditions, driven by catchment terrestrialization, peatland expansion and hydrological isolation. The present dystrophic state reflects long-term natural development, demonstrating that mountain lake dystrophication is locally controlled by catchment and hydrological changes.
Share