Tracking Fish Introduction in a Mountain Lake over the Last 200 Years Using Chironomids, Diatoms, and Cladoceran Remains
We analysed a 24 cm long sediment sequence (past ~200 years) from an alpine lake (Tatra Mts., Slovakia) for chironomids, cladocerans, and diatoms to reconstruct the effects of a historically documented fish introduction. Our results indicate that fish introduction predated the age of the sequence, a...
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Veröffentlicht in: | Water (Basel) 2023-04, Vol.15 (7), p.1372 |
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creator | Slobodníková, Veronika Hamerlík, Ladislav Wojewódka-Przybył, Marta Sochuliaková, Lucia Szarlowicz, Katarzyna Buczkó, Krisztina Chamutiová, Tímea Sedlačková Přidalová, Marcela Bitušík, Peter |
description | We analysed a 24 cm long sediment sequence (past ~200 years) from an alpine lake (Tatra Mts., Slovakia) for chironomids, cladocerans, and diatoms to reconstruct the effects of a historically documented fish introduction. Our results indicate that fish introduction predated the age of the sequence, and thus, we did not cover the lake’s fishless period. The individual proxies coincide in showing two main lake development stages. The first stage lasted until ~1950 CE and was interpreted as the stage when brown trout and alpine bullhead co-occurred. The extremely low concentration of cladocerans, the dominance of small-bodied chydorids, and the low share of daphnids, together with the low proportion/absence of large-bodied tanypod chironomids, suggest a strong effect of both species. The beginning of the next stage is probably related to the ban on fish manipulations and grazing in the catchment. A significant increase in the total abundance of cladocerans and of daphnids may indicate the extirpation of trout. The steep increase in thermally plastic chironomid taxa since the end of the 20th century indicates climate warming. Generally, while cladocerans primarily indicate fish manipulations, chironomids and diatoms mainly reflect other local and global environmental stressors. |
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Our results indicate that fish introduction predated the age of the sequence, and thus, we did not cover the lake’s fishless period. The individual proxies coincide in showing two main lake development stages. The first stage lasted until ~1950 CE and was interpreted as the stage when brown trout and alpine bullhead co-occurred. The extremely low concentration of cladocerans, the dominance of small-bodied chydorids, and the low share of daphnids, together with the low proportion/absence of large-bodied tanypod chironomids, suggest a strong effect of both species. The beginning of the next stage is probably related to the ban on fish manipulations and grazing in the catchment. A significant increase in the total abundance of cladocerans and of daphnids may indicate the extirpation of trout. The steep increase in thermally plastic chironomid taxa since the end of the 20th century indicates climate warming. Generally, while cladocerans primarily indicate fish manipulations, chironomids and diatoms mainly reflect other local and global environmental stressors.</description><identifier>ISSN: 2073-4441</identifier><identifier>EISSN: 2073-4441</identifier><identifier>DOI: 10.3390/w15071372</identifier><language>eng</language><publisher>Basel: MDPI AG</publisher><subject>20th century ; Acidification ; Bacillariophyceae ; Biodiversity ; Climate change ; Environmental stress ; Fish ; Fish stocking ; Fishes ; Global warming ; Lakes ; Marine microorganisms ; Mountain lakes ; Mountains ; Nonnative species ; Pollutants ; Sediments ; Trout</subject><ispartof>Water (Basel), 2023-04, Vol.15 (7), p.1372</ispartof><rights>COPYRIGHT 2023 MDPI AG</rights><rights>2023 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/). 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Generally, while cladocerans primarily indicate fish manipulations, chironomids and diatoms mainly reflect other local and global environmental stressors.</description><subject>20th century</subject><subject>Acidification</subject><subject>Bacillariophyceae</subject><subject>Biodiversity</subject><subject>Climate change</subject><subject>Environmental stress</subject><subject>Fish</subject><subject>Fish stocking</subject><subject>Fishes</subject><subject>Global warming</subject><subject>Lakes</subject><subject>Marine microorganisms</subject><subject>Mountain lakes</subject><subject>Mountains</subject><subject>Nonnative species</subject><subject>Pollutants</subject><subject>Sediments</subject><subject>Trout</subject><issn>2073-4441</issn><issn>2073-4441</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><recordid>eNpNUU1LAzEQDaJgqT34DwKeBFuTTbppjqVaLVQEaQ-elpjMtmm7SU2yfvx7UyrizGHeDG_ewBuELikZMCbJ7ScdEkGZKE5QpyCC9Tnn9PQfPke9GDckB5ej0ZB00NciKL21boWnNq7xzKXgTauT9Q5bhxV-8q1LKsO52gL2HxBwWkPuYsIFIfgVVIh4GQ8Sk7UN3vnGmniD76xKvslAOYMnO2W8hqAcfoEmy8ULdFarXYTeb-2i5fR-MXnsz58fZpPxvK8Zo6kvjOR1LUooeF2CHhFJBJFUUcEMZ4qXpSylZty8Gai1BC6goLIQUplySGnJuujqqLsP_r2FmKqNb4PLJ6vMkoJJWh5YgyNrpXZQWVf7lH3JaaCx2juobZ6PxbBgtGDZzi66Pi7o4GMMUFf7YBsVvitKqsMzqr9nsB9EwHnM</recordid><startdate>20230401</startdate><enddate>20230401</enddate><creator>Slobodníková, Veronika</creator><creator>Hamerlík, Ladislav</creator><creator>Wojewódka-Przybył, Marta</creator><creator>Sochuliaková, Lucia</creator><creator>Szarlowicz, Katarzyna</creator><creator>Buczkó, Krisztina</creator><creator>Chamutiová, Tímea</creator><creator>Sedlačková Přidalová, Marcela</creator><creator>Bitušík, Peter</creator><general>MDPI AG</general><scope>AAYXX</scope><scope>CITATION</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>PIMPY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><orcidid>https://orcid.org/0000-0001-9459-8311</orcidid><orcidid>https://orcid.org/0000-0002-2880-3185</orcidid><orcidid>https://orcid.org/0000-0002-0803-8981</orcidid><orcidid>https://orcid.org/0000-0002-0380-6961</orcidid><orcidid>https://orcid.org/0000-0003-4098-5791</orcidid></search><sort><creationdate>20230401</creationdate><title>Tracking Fish Introduction in a Mountain Lake over the Last 200 Years Using Chironomids, Diatoms, and Cladoceran Remains</title><author>Slobodníková, Veronika ; Hamerlík, Ladislav ; Wojewódka-Przybył, Marta ; Sochuliaková, Lucia ; Szarlowicz, Katarzyna ; Buczkó, Krisztina ; Chamutiová, Tímea ; Sedlačková Přidalová, Marcela ; Bitušík, Peter</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c331t-7d94ff76e24f6ec80907091a173d43a466969c34dbdefc9e47e219279ad651163</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2023</creationdate><topic>20th century</topic><topic>Acidification</topic><topic>Bacillariophyceae</topic><topic>Biodiversity</topic><topic>Climate change</topic><topic>Environmental stress</topic><topic>Fish</topic><topic>Fish stocking</topic><topic>Fishes</topic><topic>Global warming</topic><topic>Lakes</topic><topic>Marine microorganisms</topic><topic>Mountain lakes</topic><topic>Mountains</topic><topic>Nonnative species</topic><topic>Pollutants</topic><topic>Sediments</topic><topic>Trout</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Slobodníková, Veronika</creatorcontrib><creatorcontrib>Hamerlík, Ladislav</creatorcontrib><creatorcontrib>Wojewódka-Przybył, Marta</creatorcontrib><creatorcontrib>Sochuliaková, Lucia</creatorcontrib><creatorcontrib>Szarlowicz, Katarzyna</creatorcontrib><creatorcontrib>Buczkó, Krisztina</creatorcontrib><creatorcontrib>Chamutiová, Tímea</creatorcontrib><creatorcontrib>Sedlačková Přidalová, Marcela</creatorcontrib><creatorcontrib>Bitušík, Peter</creatorcontrib><collection>CrossRef</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest Central UK/Ireland</collection><collection>ProQuest Central Essentials</collection><collection>ProQuest Central</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>Publicly Available Content Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>ProQuest Central China</collection><jtitle>Water (Basel)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Slobodníková, Veronika</au><au>Hamerlík, Ladislav</au><au>Wojewódka-Przybył, Marta</au><au>Sochuliaková, Lucia</au><au>Szarlowicz, Katarzyna</au><au>Buczkó, Krisztina</au><au>Chamutiová, Tímea</au><au>Sedlačková Přidalová, Marcela</au><au>Bitušík, Peter</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Tracking Fish Introduction in a Mountain Lake over the Last 200 Years Using Chironomids, Diatoms, and Cladoceran Remains</atitle><jtitle>Water (Basel)</jtitle><date>2023-04-01</date><risdate>2023</risdate><volume>15</volume><issue>7</issue><spage>1372</spage><pages>1372-</pages><issn>2073-4441</issn><eissn>2073-4441</eissn><abstract>We analysed a 24 cm long sediment sequence (past ~200 years) from an alpine lake (Tatra Mts., Slovakia) for chironomids, cladocerans, and diatoms to reconstruct the effects of a historically documented fish introduction. Our results indicate that fish introduction predated the age of the sequence, and thus, we did not cover the lake’s fishless period. The individual proxies coincide in showing two main lake development stages. The first stage lasted until ~1950 CE and was interpreted as the stage when brown trout and alpine bullhead co-occurred. The extremely low concentration of cladocerans, the dominance of small-bodied chydorids, and the low share of daphnids, together with the low proportion/absence of large-bodied tanypod chironomids, suggest a strong effect of both species. The beginning of the next stage is probably related to the ban on fish manipulations and grazing in the catchment. A significant increase in the total abundance of cladocerans and of daphnids may indicate the extirpation of trout. The steep increase in thermally plastic chironomid taxa since the end of the 20th century indicates climate warming. Generally, while cladocerans primarily indicate fish manipulations, chironomids and diatoms mainly reflect other local and global environmental stressors.</abstract><cop>Basel</cop><pub>MDPI AG</pub><doi>10.3390/w15071372</doi><orcidid>https://orcid.org/0000-0001-9459-8311</orcidid><orcidid>https://orcid.org/0000-0002-2880-3185</orcidid><orcidid>https://orcid.org/0000-0002-0803-8981</orcidid><orcidid>https://orcid.org/0000-0002-0380-6961</orcidid><orcidid>https://orcid.org/0000-0003-4098-5791</orcidid><oa>free_for_read</oa></addata></record> |
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subjects | 20th century Acidification Bacillariophyceae Biodiversity Climate change Environmental stress Fish Fish stocking Fishes Global warming Lakes Marine microorganisms Mountain lakes Mountains Nonnative species Pollutants Sediments Trout |
title | Tracking Fish Introduction in a Mountain Lake over the Last 200 Years Using Chironomids, Diatoms, and Cladoceran Remains |
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