Nitrogen Uptake During Fall, Winter and Spring Differs Among Plant Functional Groups in a Subarctic Heath Ecosystem
Nitrogen (N) is a critical resource for plant growth in tundra ecosystems, and species differences in the timing of N uptake may be an important feature regulating community composition and ecosystem productivity. We added 15 N-labelled glycine to a subarctic heath tundra dominated by dwarf shrubs,...
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Veröffentlicht in: | Ecosystems (New York) 2012-09, Vol.15 (6), p.927-939 |
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description | Nitrogen (N) is a critical resource for plant growth in tundra ecosystems, and species differences in the timing of N uptake may be an important feature regulating community composition and ecosystem productivity. We added 15 N-labelled glycine to a subarctic heath tundra dominated by dwarf shrubs, mosses and graminoids in fall, and investigated its partitioning among ecosystem components at several time points (October, November, April, May, June) through to the following spring/early summer. Soil microbes had acquired 65 ± 7% of the 15 N tracer by October, but this pool decreased through winter to 37 ± 7% by April indicating significant microbial N turnover prior to spring thaw. Only the evergreen dwarf shrubs showed active 15 N acquisition before early May indicating that they had the highest potential of all functional groups for acquiring nutrients that became available in early spring. The faster-growing deciduous shrubs did not resume 15 N acquisition until after early May indicating that they relied more on nitrogen made available later during the spring/early summer. The graminoids and mosses had no significant increases in 15 N tracer recovery or tissue 15 N tracer concentrations after the first harvest in October. However, the graminoids had the highest root 15 N, tracer concentrations of all functional groups in October indicating that they primarily relied on N made available during summer and fall. Our results suggest a temporal differentiation among plant functional groups in the post-winter resumption of N uptake with evergreen dwarf shrubs having the highest potential for early N uptake, followed by deciduous dwarf shrubs and graminoids. |
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We added 15 N-labelled glycine to a subarctic heath tundra dominated by dwarf shrubs, mosses and graminoids in fall, and investigated its partitioning among ecosystem components at several time points (October, November, April, May, June) through to the following spring/early summer. Soil microbes had acquired 65 ± 7% of the 15 N tracer by October, but this pool decreased through winter to 37 ± 7% by April indicating significant microbial N turnover prior to spring thaw. Only the evergreen dwarf shrubs showed active 15 N acquisition before early May indicating that they had the highest potential of all functional groups for acquiring nutrients that became available in early spring. The faster-growing deciduous shrubs did not resume 15 N acquisition until after early May indicating that they relied more on nitrogen made available later during the spring/early summer. The graminoids and mosses had no significant increases in 15 N tracer recovery or tissue 15 N tracer concentrations after the first harvest in October. However, the graminoids had the highest root 15 N, tracer concentrations of all functional groups in October indicating that they primarily relied on N made available during summer and fall. Our results suggest a temporal differentiation among plant functional groups in the post-winter resumption of N uptake with evergreen dwarf shrubs having the highest potential for early N uptake, followed by deciduous dwarf shrubs and graminoids.</description><identifier>ISSN: 1432-9840</identifier><identifier>EISSN: 1435-0629</identifier><identifier>DOI: 10.1007/s10021-012-9555-x</identifier><language>eng</language><publisher>New York: Springer Science+Business Media</publisher><subject>Acid soils ; Agricultural soils ; Agrology ; Biogeochemistry ; Biomass ; Biomedical and Life Sciences ; Community composition ; Ecology ; Ecosystem components ; Ecosystems ; Environmental Management ; Forest soils ; Geoecology/Natural Processes ; Glycine ; Hydrology/Water Resources ; Life Sciences ; Microbial biomass ; Mosses ; Nitrogen ; Nutrient availability ; Plant ecology ; Plant growth ; Plant Sciences ; Plants ; Shrubs ; Soil ecology ; Soil microbiology ; Soil microorganisms ; Spring ; Summer ; Terrestrial ecosystems ; Tracers (Biology) ; Tundra ; Tundra ecology ; Tundra soils ; Winter ; Zoology</subject><ispartof>Ecosystems (New York), 2012-09, Vol.15 (6), p.927-939</ispartof><rights>2012 Springer Science+Business Media, LLC</rights><rights>Springer Science+Business Media, LLC 2012</rights><rights>COPYRIGHT 2012 Springer</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c410t-72cdbff444930d21e2cfe954e211edc76d200d31696a1172f5ef50926ba403e73</citedby><cites>FETCH-LOGICAL-c410t-72cdbff444930d21e2cfe954e211edc76d200d31696a1172f5ef50926ba403e73</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/23253734$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/23253734$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,803,27924,27925,41488,42557,51319,58017,58250</link.rule.ids></links><search><creatorcontrib>Larsen, Klaus S.</creatorcontrib><creatorcontrib>Michelsen, Anders</creatorcontrib><creatorcontrib>Jonasson, Sven</creatorcontrib><creatorcontrib>Beier, Claus</creatorcontrib><creatorcontrib>Grogan, Paul</creatorcontrib><title>Nitrogen Uptake During Fall, Winter and Spring Differs Among Plant Functional Groups in a Subarctic Heath Ecosystem</title><title>Ecosystems (New York)</title><addtitle>Ecosystems</addtitle><description>Nitrogen (N) is a critical resource for plant growth in tundra ecosystems, and species differences in the timing of N uptake may be an important feature regulating community composition and ecosystem productivity. We added 15 N-labelled glycine to a subarctic heath tundra dominated by dwarf shrubs, mosses and graminoids in fall, and investigated its partitioning among ecosystem components at several time points (October, November, April, May, June) through to the following spring/early summer. Soil microbes had acquired 65 ± 7% of the 15 N tracer by October, but this pool decreased through winter to 37 ± 7% by April indicating significant microbial N turnover prior to spring thaw. Only the evergreen dwarf shrubs showed active 15 N acquisition before early May indicating that they had the highest potential of all functional groups for acquiring nutrients that became available in early spring. The faster-growing deciduous shrubs did not resume 15 N acquisition until after early May indicating that they relied more on nitrogen made available later during the spring/early summer. The graminoids and mosses had no significant increases in 15 N tracer recovery or tissue 15 N tracer concentrations after the first harvest in October. However, the graminoids had the highest root 15 N, tracer concentrations of all functional groups in October indicating that they primarily relied on N made available during summer and fall. Our results suggest a temporal differentiation among plant functional groups in the post-winter resumption of N uptake with evergreen dwarf shrubs having the highest potential for early N uptake, followed by deciduous dwarf shrubs and graminoids.</description><subject>Acid soils</subject><subject>Agricultural soils</subject><subject>Agrology</subject><subject>Biogeochemistry</subject><subject>Biomass</subject><subject>Biomedical and Life Sciences</subject><subject>Community composition</subject><subject>Ecology</subject><subject>Ecosystem components</subject><subject>Ecosystems</subject><subject>Environmental Management</subject><subject>Forest soils</subject><subject>Geoecology/Natural Processes</subject><subject>Glycine</subject><subject>Hydrology/Water Resources</subject><subject>Life Sciences</subject><subject>Microbial biomass</subject><subject>Mosses</subject><subject>Nitrogen</subject><subject>Nutrient availability</subject><subject>Plant ecology</subject><subject>Plant growth</subject><subject>Plant Sciences</subject><subject>Plants</subject><subject>Shrubs</subject><subject>Soil ecology</subject><subject>Soil microbiology</subject><subject>Soil microorganisms</subject><subject>Spring</subject><subject>Summer</subject><subject>Terrestrial ecosystems</subject><subject>Tracers (Biology)</subject><subject>Tundra</subject><subject>Tundra ecology</subject><subject>Tundra soils</subject><subject>Winter</subject><subject>Zoology</subject><issn>1432-9840</issn><issn>1435-0629</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2012</creationdate><recordtype>article</recordtype><sourceid>8G5</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><sourceid>GUQSH</sourceid><sourceid>M2O</sourceid><recordid>eNp1UV1LHDEUHUoLtdof0IdCoC99cDSfE_O4qKsFsQUrfQzZzM2adSbZJhnQf292pxQplEByc-85NzfnNM0ngk8IxvI0152SFhPaKiFE-_SmOSCciRZ3VL3dx7VyxvH75kPOG4yJOOP8oMm3vqS4hoDut8U8ArqYkg9rtDTDcIx--VAgIRN6dLfd5y-8c5AyWoyx3n4MJhS0nIItPgYzoKsUp21GPiCD7qaVSbVg0TWY8oAubczPucB41LxzZsjw8c952NwvL3-eX7c336--nS9uWssJLq2ktl85xzlXDPeUALUOlOBACYHeyq6nGPeMdKozhEjqBDiBFe1WhmMGkh02X-e-2xR_T5CLHn22MNShIU5ZE9wpWoVQqkK__APdxCnVH-1QTNKOS8wr6mRGrc0A2gcXSzK2rh5Gb2MA52t-IQmTDBO5I5CZYFPMOYHTVcXRpOfaVe9807Nvuvqmd77pp8qhMyfvFYf0epT_kz7PpE0uMf19hTIq6iycvQDQhKOS</recordid><startdate>20120901</startdate><enddate>20120901</enddate><creator>Larsen, Klaus S.</creator><creator>Michelsen, Anders</creator><creator>Jonasson, Sven</creator><creator>Beier, Claus</creator><creator>Grogan, Paul</creator><general>Springer Science+Business Media</general><general>Springer-Verlag</general><general>Springer</general><general>Springer Nature B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7SN</scope><scope>7ST</scope><scope>7XB</scope><scope>88I</scope><scope>8FK</scope><scope>8G5</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>HCIFZ</scope><scope>M2O</scope><scope>M2P</scope><scope>MBDVC</scope><scope>PATMY</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>SOI</scope></search><sort><creationdate>20120901</creationdate><title>Nitrogen Uptake During Fall, Winter and Spring Differs Among Plant Functional Groups in a Subarctic Heath Ecosystem</title><author>Larsen, Klaus S. ; Michelsen, Anders ; Jonasson, Sven ; Beier, Claus ; Grogan, Paul</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c410t-72cdbff444930d21e2cfe954e211edc76d200d31696a1172f5ef50926ba403e73</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2012</creationdate><topic>Acid soils</topic><topic>Agricultural soils</topic><topic>Agrology</topic><topic>Biogeochemistry</topic><topic>Biomass</topic><topic>Biomedical and Life Sciences</topic><topic>Community composition</topic><topic>Ecology</topic><topic>Ecosystem components</topic><topic>Ecosystems</topic><topic>Environmental Management</topic><topic>Forest soils</topic><topic>Geoecology/Natural Processes</topic><topic>Glycine</topic><topic>Hydrology/Water Resources</topic><topic>Life Sciences</topic><topic>Microbial biomass</topic><topic>Mosses</topic><topic>Nitrogen</topic><topic>Nutrient availability</topic><topic>Plant ecology</topic><topic>Plant growth</topic><topic>Plant Sciences</topic><topic>Plants</topic><topic>Shrubs</topic><topic>Soil ecology</topic><topic>Soil microbiology</topic><topic>Soil microorganisms</topic><topic>Spring</topic><topic>Summer</topic><topic>Terrestrial ecosystems</topic><topic>Tracers (Biology)</topic><topic>Tundra</topic><topic>Tundra ecology</topic><topic>Tundra soils</topic><topic>Winter</topic><topic>Zoology</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Larsen, Klaus S.</creatorcontrib><creatorcontrib>Michelsen, Anders</creatorcontrib><creatorcontrib>Jonasson, Sven</creatorcontrib><creatorcontrib>Beier, Claus</creatorcontrib><creatorcontrib>Grogan, Paul</creatorcontrib><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>ProQuest Central (purchase pre-March 2016)</collection><collection>Science Database (Alumni Edition)</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>Research Library (Alumni Edition)</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest Central UK/Ireland</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>ProQuest Central</collection><collection>Natural Science Collection (ProQuest)</collection><collection>Earth, Atmospheric & Aquatic Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>ProQuest Central Student</collection><collection>Research Library Prep</collection><collection>SciTech Premium Collection</collection><collection>Research Library</collection><collection>Science Database (ProQuest)</collection><collection>Research Library (Corporate)</collection><collection>Environmental Science Database</collection><collection>Earth, Atmospheric & Aquatic 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>ProQuest Central Basic</collection><collection>Environment Abstracts</collection><jtitle>Ecosystems (New York)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Larsen, Klaus S.</au><au>Michelsen, Anders</au><au>Jonasson, Sven</au><au>Beier, Claus</au><au>Grogan, Paul</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Nitrogen Uptake During Fall, Winter and Spring Differs Among Plant Functional Groups in a Subarctic Heath Ecosystem</atitle><jtitle>Ecosystems (New York)</jtitle><stitle>Ecosystems</stitle><date>2012-09-01</date><risdate>2012</risdate><volume>15</volume><issue>6</issue><spage>927</spage><epage>939</epage><pages>927-939</pages><issn>1432-9840</issn><eissn>1435-0629</eissn><abstract>Nitrogen (N) is a critical resource for plant growth in tundra ecosystems, and species differences in the timing of N uptake may be an important feature regulating community composition and ecosystem productivity. We added 15 N-labelled glycine to a subarctic heath tundra dominated by dwarf shrubs, mosses and graminoids in fall, and investigated its partitioning among ecosystem components at several time points (October, November, April, May, June) through to the following spring/early summer. Soil microbes had acquired 65 ± 7% of the 15 N tracer by October, but this pool decreased through winter to 37 ± 7% by April indicating significant microbial N turnover prior to spring thaw. Only the evergreen dwarf shrubs showed active 15 N acquisition before early May indicating that they had the highest potential of all functional groups for acquiring nutrients that became available in early spring. The faster-growing deciduous shrubs did not resume 15 N acquisition until after early May indicating that they relied more on nitrogen made available later during the spring/early summer. The graminoids and mosses had no significant increases in 15 N tracer recovery or tissue 15 N tracer concentrations after the first harvest in October. However, the graminoids had the highest root 15 N, tracer concentrations of all functional groups in October indicating that they primarily relied on N made available during summer and fall. Our results suggest a temporal differentiation among plant functional groups in the post-winter resumption of N uptake with evergreen dwarf shrubs having the highest potential for early N uptake, followed by deciduous dwarf shrubs and graminoids.</abstract><cop>New York</cop><pub>Springer Science+Business Media</pub><doi>10.1007/s10021-012-9555-x</doi><tpages>13</tpages></addata></record> |
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subjects | Acid soils Agricultural soils Agrology Biogeochemistry Biomass Biomedical and Life Sciences Community composition Ecology Ecosystem components Ecosystems Environmental Management Forest soils Geoecology/Natural Processes Glycine Hydrology/Water Resources Life Sciences Microbial biomass Mosses Nitrogen Nutrient availability Plant ecology Plant growth Plant Sciences Plants Shrubs Soil ecology Soil microbiology Soil microorganisms Spring Summer Terrestrial ecosystems Tracers (Biology) Tundra Tundra ecology Tundra soils Winter Zoology |
title | Nitrogen Uptake During Fall, Winter and Spring Differs Among Plant Functional Groups in a Subarctic Heath Ecosystem |
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