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Zooplankton in Lake Atnsjøen 1985–1997
Issue Title: The Atna River: Studies in an Alpine-Boreal Watershed The aim of this paper is to study long-term changes in the zooplankton of a subalpine locality unaffected by direct anthropogenic disturbances. The material has been collected during the period 1985-1997; since 1988 a standardised sa...
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Published in: | Hydrobiologia 2004-06, Vol.521 (1-3), p.149-175 |
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description | Issue Title: The Atna River: Studies in an Alpine-Boreal Watershed The aim of this paper is to study long-term changes in the zooplankton of a subalpine locality unaffected by direct anthropogenic disturbances. The material has been collected during the period 1985-1997; since 1988 a standardised sampling program has been followed, with five sampling dates during the ice free period (June-October) at three fixed stations. Altogether 17 species of Rotatoria, 9 species of Copepoda and 11 species of Cladocera were recorded. Of these 10 species of Rotatoria, two species of Copepoda and five species of Cladocera occur regularly in the plankton. Polyarthra vulgaris dominate among the rotifers together with Kellicottia longispina and Conochilus unicornis. The crustacean community is dominated by the copepod Cyclops scutifer, and the cladocerans Bosmina longispina, Holopedium gibberum and Daphnia longispina. The cladocerans Bythotrephes longimanus, Polyphemus pediculus,and the copepodsArctodiaptomus laticeps and Heterocope saliens all occur regularly, but at low densities. The zooplankton density is low in May/June and peaks in August and September, but the timing of maximum densities varies from year to year. By numbers, the rotifers strongly dominate with densities 10-15 times higher than the crustaceans. The annual maximum density (rotifers plus crustaceans) ranged from 50 ind. l^sup -1^ (1985, 1988) to 450 ind. l^sup -1^ (1995). Mean density is about 140-150 ind. l^sup -1^. By biomass (dry weight), the cladocerans constitute 60%, while the copepods and rotifers constitute 30% and 10% of the zooplankton, respectively. The annual maximum has varied between 70 and 260 μg dw l^sup -1^, with 170 μg dw l^sup -1^ as the mean level. C. scutifer usually has a one-year lifecycle without diapause, but a small fraction of the population has a two-year lifecycle. The life cycle in 1989 and 1990 differed strongly from the other years. The life cycles of B. longispina, D. longispina and possibly also H. gibberum and A. laticeps, indicate two generations during the summer. H. gibberumandH. saliens pass the winter as resting eggs. The other crustacean species, except C. scutifer, pass the winter mainly as resting eggs, but all have a small winter population in the water mass. C. scutifer is the only species without resting eggs. The vertical distribution normally shows highest density between 5 and 10 m depth. However, during some periods maximum density is observed close to t |
doi_str_mv | 10.1023/B:HYDR.0000026357.80231.d2 |
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The material has been collected during the period 1985-1997; since 1988 a standardised sampling program has been followed, with five sampling dates during the ice free period (June-October) at three fixed stations. Altogether 17 species of Rotatoria, 9 species of Copepoda and 11 species of Cladocera were recorded. Of these 10 species of Rotatoria, two species of Copepoda and five species of Cladocera occur regularly in the plankton. Polyarthra vulgaris dominate among the rotifers together with Kellicottia longispina and Conochilus unicornis. The crustacean community is dominated by the copepod Cyclops scutifer, and the cladocerans Bosmina longispina, Holopedium gibberum and Daphnia longispina. The cladocerans Bythotrephes longimanus, Polyphemus pediculus,and the copepodsArctodiaptomus laticeps and Heterocope saliens all occur regularly, but at low densities. The zooplankton density is low in May/June and peaks in August and September, but the timing of maximum densities varies from year to year. By numbers, the rotifers strongly dominate with densities 10-15 times higher than the crustaceans. The annual maximum density (rotifers plus crustaceans) ranged from 50 ind. l^sup -1^ (1985, 1988) to 450 ind. l^sup -1^ (1995). Mean density is about 140-150 ind. l^sup -1^. By biomass (dry weight), the cladocerans constitute 60%, while the copepods and rotifers constitute 30% and 10% of the zooplankton, respectively. The annual maximum has varied between 70 and 260 μg dw l^sup -1^, with 170 μg dw l^sup -1^ as the mean level. C. scutifer usually has a one-year lifecycle without diapause, but a small fraction of the population has a two-year lifecycle. The life cycle in 1989 and 1990 differed strongly from the other years. The life cycles of B. longispina, D. longispina and possibly also H. gibberum and A. laticeps, indicate two generations during the summer. H. gibberumandH. saliens pass the winter as resting eggs. The other crustacean species, except C. scutifer, pass the winter mainly as resting eggs, but all have a small winter population in the water mass. C. scutifer is the only species without resting eggs. The vertical distribution normally shows highest density between 5 and 10 m depth. However, during some periods maximum density is observed close to the surface, while at other times it is seen deep in the hypolimnion. The vertical distribution is most pronounced when the thermocline is sharp, and less pronounced during the full circulation in autumn. The vertical migration may also be pronounced, especially in B. longispina, with high density near the surface during the night. The vertical migration is less pronounced among the rotifers and copepods. The degree of vertical migration varies with temperature and food conditions. There is little variation from year to year in species composition, but large variation in species dominance, seasonal development, population density, and vertical and horizontal distribution during the sampling period. Variations in temperature, food condition, predation, and water through-flow are possible causes for the observed differences between the years. Input of allochthonous material is especially important. However, no clear correlation have been found between the development of the plankton community and these environmental factors. Hence, these interactions are complex and multifactorial.[PUBLICATION ABSTRACT]</description><identifier>ISSN: 0018-8158</identifier><identifier>EISSN: 1573-5117</identifier><identifier>DOI: 10.1023/B:HYDR.0000026357.80231.d2</identifier><language>eng</language><publisher>Dordrecht: Springer Nature B.V</publisher><subject>Anthropogenic factors ; Arctodiaptomus laticeps ; Bosmina longispina ; Bythotrephes longimanus ; Cladocera ; Conochilus unicornis ; Copepoda ; Crustaceans ; Cyclops scutifer ; Daphnia longispina ; Eggs ; Environmental factors ; Freshwater ; Heterocope saliens ; Holopedium gibberum ; Hypolimnion ; Kellicottia longispina ; Life cycles ; Plankton ; Polyarthra vulgaris ; Polyphemus pediculus ; Population density ; Rotifera ; Species composition ; Thermocline ; Vertical distribution ; Winter ; Zooplankton</subject><ispartof>Hydrobiologia, 2004-06, Vol.521 (1-3), p.149-175</ispartof><rights>Kluwer Academic Publishers 2004</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c350t-43d8c09dd142aa6fe172af7cec9fad32178f14e0a324333e10ca4405d85e10133</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27903,27904</link.rule.ids></links><search><creatorcontrib>Halvorsen, Gunnar</creatorcontrib><creatorcontrib>Dervo, Børre K.</creatorcontrib><creatorcontrib>Papinska, Katarzyna</creatorcontrib><title>Zooplankton in Lake Atnsjøen 1985–1997</title><title>Hydrobiologia</title><description>Issue Title: The Atna River: Studies in an Alpine-Boreal Watershed The aim of this paper is to study long-term changes in the zooplankton of a subalpine locality unaffected by direct anthropogenic disturbances. The material has been collected during the period 1985-1997; since 1988 a standardised sampling program has been followed, with five sampling dates during the ice free period (June-October) at three fixed stations. Altogether 17 species of Rotatoria, 9 species of Copepoda and 11 species of Cladocera were recorded. Of these 10 species of Rotatoria, two species of Copepoda and five species of Cladocera occur regularly in the plankton. Polyarthra vulgaris dominate among the rotifers together with Kellicottia longispina and Conochilus unicornis. The crustacean community is dominated by the copepod Cyclops scutifer, and the cladocerans Bosmina longispina, Holopedium gibberum and Daphnia longispina. The cladocerans Bythotrephes longimanus, Polyphemus pediculus,and the copepodsArctodiaptomus laticeps and Heterocope saliens all occur regularly, but at low densities. The zooplankton density is low in May/June and peaks in August and September, but the timing of maximum densities varies from year to year. By numbers, the rotifers strongly dominate with densities 10-15 times higher than the crustaceans. The annual maximum density (rotifers plus crustaceans) ranged from 50 ind. l^sup -1^ (1985, 1988) to 450 ind. l^sup -1^ (1995). Mean density is about 140-150 ind. l^sup -1^. By biomass (dry weight), the cladocerans constitute 60%, while the copepods and rotifers constitute 30% and 10% of the zooplankton, respectively. The annual maximum has varied between 70 and 260 μg dw l^sup -1^, with 170 μg dw l^sup -1^ as the mean level. C. scutifer usually has a one-year lifecycle without diapause, but a small fraction of the population has a two-year lifecycle. The life cycle in 1989 and 1990 differed strongly from the other years. The life cycles of B. longispina, D. longispina and possibly also H. gibberum and A. laticeps, indicate two generations during the summer. H. gibberumandH. saliens pass the winter as resting eggs. The other crustacean species, except C. scutifer, pass the winter mainly as resting eggs, but all have a small winter population in the water mass. C. scutifer is the only species without resting eggs. The vertical distribution normally shows highest density between 5 and 10 m depth. However, during some periods maximum density is observed close to the surface, while at other times it is seen deep in the hypolimnion. The vertical distribution is most pronounced when the thermocline is sharp, and less pronounced during the full circulation in autumn. The vertical migration may also be pronounced, especially in B. longispina, with high density near the surface during the night. The vertical migration is less pronounced among the rotifers and copepods. The degree of vertical migration varies with temperature and food conditions. There is little variation from year to year in species composition, but large variation in species dominance, seasonal development, population density, and vertical and horizontal distribution during the sampling period. Variations in temperature, food condition, predation, and water through-flow are possible causes for the observed differences between the years. Input of allochthonous material is especially important. However, no clear correlation have been found between the development of the plankton community and these environmental factors. Hence, these interactions are complex and multifactorial.[PUBLICATION ABSTRACT]</description><subject>Anthropogenic factors</subject><subject>Arctodiaptomus laticeps</subject><subject>Bosmina longispina</subject><subject>Bythotrephes longimanus</subject><subject>Cladocera</subject><subject>Conochilus unicornis</subject><subject>Copepoda</subject><subject>Crustaceans</subject><subject>Cyclops scutifer</subject><subject>Daphnia longispina</subject><subject>Eggs</subject><subject>Environmental factors</subject><subject>Freshwater</subject><subject>Heterocope saliens</subject><subject>Holopedium gibberum</subject><subject>Hypolimnion</subject><subject>Kellicottia longispina</subject><subject>Life cycles</subject><subject>Plankton</subject><subject>Polyarthra vulgaris</subject><subject>Polyphemus pediculus</subject><subject>Population density</subject><subject>Rotifera</subject><subject>Species composition</subject><subject>Thermocline</subject><subject>Vertical distribution</subject><subject>Winter</subject><subject>Zooplankton</subject><issn>0018-8158</issn><issn>1573-5117</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2004</creationdate><recordtype>article</recordtype><recordid>eNqFkM9KAzEQh4MoWKvvsPQgeNg1k0mapLe2_qlQEEQPegkhm4Vu203dbA_efAdfxrtv4pO4awXBi3OZ4cfHMPMRMgCaAWV4PhnNHi_uMtoVG6KQmWpjyHK2R3ogJKYCQO6THqWgUgVCHZKjGMsWl5rRHjl7CmGzstWyCVWyqJK5Xfpk3FSx_Hj3VQJaic_XN9BaHpODwq6iP_npffJwdXk_naXz2-ub6XieOhS0STnmylGd58CZtcPCg2S2kM47XdgcGUhVAPfUIuOI6IE6yzkVuRLtDIh9crrbu6nD89bHxqwX0flVe6QP22hAUS4Bhv-DXFKtEFpw8Acsw7au2ieMYsA4MOig0Q5ydYix9oXZ1Iu1rV8MUNO5NhPTuTa_rs23a5Mz_ALCJXCq</recordid><startdate>20040601</startdate><enddate>20040601</enddate><creator>Halvorsen, Gunnar</creator><creator>Dervo, Børre K.</creator><creator>Papinska, Katarzyna</creator><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7QG</scope><scope>7QH</scope><scope>7SN</scope><scope>7SS</scope><scope>7U7</scope><scope>7UA</scope><scope>88A</scope><scope>8AO</scope><scope>8FD</scope><scope>8FE</scope><scope>8FH</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>F1W</scope><scope>FR3</scope><scope>GNUQQ</scope><scope>H95</scope><scope>HCIFZ</scope><scope>L.G</scope><scope>LK8</scope><scope>M7N</scope><scope>M7P</scope><scope>P64</scope><scope>PATMY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>RC3</scope><scope>7ST</scope><scope>SOI</scope></search><sort><creationdate>20040601</creationdate><title>Zooplankton in Lake Atnsjøen 1985–1997</title><author>Halvorsen, Gunnar ; Dervo, Børre K. ; Papinska, Katarzyna</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c350t-43d8c09dd142aa6fe172af7cec9fad32178f14e0a324333e10ca4405d85e10133</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2004</creationdate><topic>Anthropogenic factors</topic><topic>Arctodiaptomus laticeps</topic><topic>Bosmina longispina</topic><topic>Bythotrephes longimanus</topic><topic>Cladocera</topic><topic>Conochilus unicornis</topic><topic>Copepoda</topic><topic>Crustaceans</topic><topic>Cyclops scutifer</topic><topic>Daphnia longispina</topic><topic>Eggs</topic><topic>Environmental factors</topic><topic>Freshwater</topic><topic>Heterocope saliens</topic><topic>Holopedium gibberum</topic><topic>Hypolimnion</topic><topic>Kellicottia longispina</topic><topic>Life cycles</topic><topic>Plankton</topic><topic>Polyarthra vulgaris</topic><topic>Polyphemus pediculus</topic><topic>Population density</topic><topic>Rotifera</topic><topic>Species composition</topic><topic>Thermocline</topic><topic>Vertical distribution</topic><topic>Winter</topic><topic>Zooplankton</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Halvorsen, Gunnar</creatorcontrib><creatorcontrib>Dervo, Børre K.</creatorcontrib><creatorcontrib>Papinska, Katarzyna</creatorcontrib><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Animal Behavior Abstracts</collection><collection>Aqualine</collection><collection>Ecology Abstracts</collection><collection>Entomology Abstracts (Full archive)</collection><collection>Toxicology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Biology Database (Alumni Edition)</collection><collection>ProQuest Pharma Collection</collection><collection>Technology Research Database</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>ProQuest Central (Alumni)</collection><collection>ProQuest One Sustainability</collection><collection>ProQuest Central</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>Biological Science Collection</collection><collection>ProQuest Central</collection><collection>Natural Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Engineering Research Database</collection><collection>ProQuest Central Student</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>SciTech Premium Collection</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>ProQuest Biological Science Collection</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biological Science Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environmental Science 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>Environmental Science Collection</collection><collection>Genetics Abstracts</collection><collection>Environment Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Hydrobiologia</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Halvorsen, Gunnar</au><au>Dervo, Børre K.</au><au>Papinska, Katarzyna</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Zooplankton in Lake Atnsjøen 1985–1997</atitle><jtitle>Hydrobiologia</jtitle><date>2004-06-01</date><risdate>2004</risdate><volume>521</volume><issue>1-3</issue><spage>149</spage><epage>175</epage><pages>149-175</pages><issn>0018-8158</issn><eissn>1573-5117</eissn><abstract>Issue Title: The Atna River: Studies in an Alpine-Boreal Watershed The aim of this paper is to study long-term changes in the zooplankton of a subalpine locality unaffected by direct anthropogenic disturbances. The material has been collected during the period 1985-1997; since 1988 a standardised sampling program has been followed, with five sampling dates during the ice free period (June-October) at three fixed stations. Altogether 17 species of Rotatoria, 9 species of Copepoda and 11 species of Cladocera were recorded. Of these 10 species of Rotatoria, two species of Copepoda and five species of Cladocera occur regularly in the plankton. Polyarthra vulgaris dominate among the rotifers together with Kellicottia longispina and Conochilus unicornis. The crustacean community is dominated by the copepod Cyclops scutifer, and the cladocerans Bosmina longispina, Holopedium gibberum and Daphnia longispina. The cladocerans Bythotrephes longimanus, Polyphemus pediculus,and the copepodsArctodiaptomus laticeps and Heterocope saliens all occur regularly, but at low densities. The zooplankton density is low in May/June and peaks in August and September, but the timing of maximum densities varies from year to year. By numbers, the rotifers strongly dominate with densities 10-15 times higher than the crustaceans. The annual maximum density (rotifers plus crustaceans) ranged from 50 ind. l^sup -1^ (1985, 1988) to 450 ind. l^sup -1^ (1995). Mean density is about 140-150 ind. l^sup -1^. By biomass (dry weight), the cladocerans constitute 60%, while the copepods and rotifers constitute 30% and 10% of the zooplankton, respectively. The annual maximum has varied between 70 and 260 μg dw l^sup -1^, with 170 μg dw l^sup -1^ as the mean level. C. scutifer usually has a one-year lifecycle without diapause, but a small fraction of the population has a two-year lifecycle. The life cycle in 1989 and 1990 differed strongly from the other years. The life cycles of B. longispina, D. longispina and possibly also H. gibberum and A. laticeps, indicate two generations during the summer. H. gibberumandH. saliens pass the winter as resting eggs. The other crustacean species, except C. scutifer, pass the winter mainly as resting eggs, but all have a small winter population in the water mass. C. scutifer is the only species without resting eggs. The vertical distribution normally shows highest density between 5 and 10 m depth. However, during some periods maximum density is observed close to the surface, while at other times it is seen deep in the hypolimnion. The vertical distribution is most pronounced when the thermocline is sharp, and less pronounced during the full circulation in autumn. The vertical migration may also be pronounced, especially in B. longispina, with high density near the surface during the night. The vertical migration is less pronounced among the rotifers and copepods. The degree of vertical migration varies with temperature and food conditions. There is little variation from year to year in species composition, but large variation in species dominance, seasonal development, population density, and vertical and horizontal distribution during the sampling period. Variations in temperature, food condition, predation, and water through-flow are possible causes for the observed differences between the years. Input of allochthonous material is especially important. However, no clear correlation have been found between the development of the plankton community and these environmental factors. Hence, these interactions are complex and multifactorial.[PUBLICATION ABSTRACT]</abstract><cop>Dordrecht</cop><pub>Springer Nature B.V</pub><doi>10.1023/B:HYDR.0000026357.80231.d2</doi><tpages>27</tpages></addata></record> |
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subjects | Anthropogenic factors Arctodiaptomus laticeps Bosmina longispina Bythotrephes longimanus Cladocera Conochilus unicornis Copepoda Crustaceans Cyclops scutifer Daphnia longispina Eggs Environmental factors Freshwater Heterocope saliens Holopedium gibberum Hypolimnion Kellicottia longispina Life cycles Plankton Polyarthra vulgaris Polyphemus pediculus Population density Rotifera Species composition Thermocline Vertical distribution Winter Zooplankton |
title | Zooplankton in Lake Atnsjøen 1985–1997 |
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