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Canopy Tree-Soil Interactions within Temperate Forests: Species Effects on Soil Carbon and Nitrogen

In a northwestern Connecticut forest, we quantified the carbon (C) and nitrogen (N) content of the forest floor and the top 15 cm of mineral soil and the rate of midsummer net N mineralization beneath six different tree species. There were large interspecific differences in forest floor depth and ma...

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Published in:Ecological applications 1998-05, Vol.8 (2), p.440-446
Main Authors: Finzi, Adrien C., Van Breemen, Nico, Canham, Charles D.
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Language:English
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description In a northwestern Connecticut forest, we quantified the carbon (C) and nitrogen (N) content of the forest floor and the top 15 cm of mineral soil and the rate of midsummer net N mineralization beneath six different tree species. There were large interspecific differences in forest floor depth and mass, in the size and distribution of C and N pools at varying soil depths, and in rates of midsummer net N mineralization and nitrification. Forest floor mass ranged from 3.2 kg/m2to 11.0 kg/m2and was smallest beneath sugar maple and largest beneath hemlock. The pool size of C in the forest floor ranged from 1.1 kg/m2to 4.4 kg/m2while the N content of the forest floor ranged from 83 g/m2to 229 g/m2. Forest floor C and N pools were smallest beneath sugar maple and highest beneath hemlock. Soil C:N ratios (range: 14.8-19.5) were lower beneath sugar maple, red maple, and white ash than beneath beech, red oak, and hemlock, whereas the opposite was true of the midsummer rate of net N mineralization (range: 0.91-2.02 g·m-2·28 d-1). The rate of net nitrification was positively correlated with the rate of net N mineralization. Interspecific differences in litter production and quality explain the large differences among species in the size of the forest floor C and N pools and in net N mineralization rates. The differences in the size and distribution of C and N pools beneath the different species suggest that the mechanisms regulating the process of species replacement in these forests will mediate the effects of anthropogenic, environmental changes in soil C and N dynamics.
doi_str_mv 10.1890/1051-0761(1998)008[0440:ctsiwt]2.0.co;2
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There were large interspecific differences in forest floor depth and mass, in the size and distribution of C and N pools at varying soil depths, and in rates of midsummer net N mineralization and nitrification. Forest floor mass ranged from 3.2 kg/m2to 11.0 kg/m2and was smallest beneath sugar maple and largest beneath hemlock. The pool size of C in the forest floor ranged from 1.1 kg/m2to 4.4 kg/m2while the N content of the forest floor ranged from 83 g/m2to 229 g/m2. Forest floor C and N pools were smallest beneath sugar maple and highest beneath hemlock. Soil C:N ratios (range: 14.8-19.5) were lower beneath sugar maple, red maple, and white ash than beneath beech, red oak, and hemlock, whereas the opposite was true of the midsummer rate of net N mineralization (range: 0.91-2.02 g·m-2·28 d-1). The rate of net nitrification was positively correlated with the rate of net N mineralization. Interspecific differences in litter production and quality explain the large differences among species in the size of the forest floor C and N pools and in net N mineralization rates. The differences in the size and distribution of C and N pools beneath the different species suggest that the mechanisms regulating the process of species replacement in these forests will mediate the effects of anthropogenic, environmental changes in soil C and N dynamics.</description><subject>carbon</subject><subject>Coniferous forests</subject><subject>ecosystem</subject><subject>forest</subject><subject>Forest ecology</subject><subject>Forest litter</subject><subject>Forest soils</subject><subject>Maple sugar</subject><subject>Mineral soils</subject><subject>Nitrification</subject><subject>Nitrogen</subject><subject>Soil ecology</subject><subject>soils, forest</subject><subject>Trees</subject><issn>1051-0761</issn><issn>1939-5582</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1998</creationdate><recordtype>article</recordtype><recordid>eNqdkVFvFCEQxzdGE2v1O_BgjD7sdYBdDupTs7nWSxqruTU-GEMoNyjN3rIFmst9e1mvJr6ZyAMM8J8fw_yr6ozCgkoFZW1pDUtB31Kl5DsA-Q2aBs5tTn6fv7MFLGx4z55UJ1RxVbetZE9L_CfrefUipTsogzF2UtnOjGE6kD4i1pvgB7IeM0Zjsw9jInuff_qR9LibymFGchkippzOyWZC6zGRlXNYniZhJL_TOxNvS2zGLfnocww_cHxZPXNmSPjqcT2tvlyu-u5DfX1zte4urmvTtALKTIVsneBUOE5hi5yVLYPGmq0FBhSVAs5xyURrFRVbhY2it1Q55wCV5KfVmyN3iuH-oZSpdz5ZHAYzYnhImkpaWqbEv4ViLmXJivDqKLQxpBTR6Sn6nYkHTUHPbui5r3ruq57d0MUNPbuhu36z_tprpkt4o2fS5yNp7wc8_C9Gry4-zQLJymVhvj4y71IO8W8m47DUrPwCJOe_AN4ApAw</recordid><startdate>199805</startdate><enddate>199805</enddate><creator>Finzi, Adrien C.</creator><creator>Van Breemen, Nico</creator><creator>Canham, Charles D.</creator><general>Ecological Society of America</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7SN</scope><scope>C1K</scope><scope>7TG</scope><scope>KL.</scope></search><sort><creationdate>199805</creationdate><title>Canopy Tree-Soil Interactions within Temperate Forests: Species Effects on Soil Carbon and Nitrogen</title><author>Finzi, Adrien C. ; Van Breemen, Nico ; Canham, Charles D.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a4560-a41685f6316f310de3285f204cadc0201e99033e7265c916d9e491b19fff0e983</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1998</creationdate><topic>carbon</topic><topic>Coniferous forests</topic><topic>ecosystem</topic><topic>forest</topic><topic>Forest ecology</topic><topic>Forest litter</topic><topic>Forest soils</topic><topic>Maple sugar</topic><topic>Mineral soils</topic><topic>Nitrification</topic><topic>Nitrogen</topic><topic>Soil ecology</topic><topic>soils, forest</topic><topic>Trees</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Finzi, Adrien C.</creatorcontrib><creatorcontrib>Van Breemen, Nico</creatorcontrib><creatorcontrib>Canham, Charles D.</creatorcontrib><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Meteorological &amp; Geoastrophysical Abstracts</collection><collection>Meteorological &amp; Geoastrophysical Abstracts - Academic</collection><jtitle>Ecological applications</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Finzi, Adrien C.</au><au>Van Breemen, Nico</au><au>Canham, Charles D.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Canopy Tree-Soil Interactions within Temperate Forests: Species Effects on Soil Carbon and Nitrogen</atitle><jtitle>Ecological applications</jtitle><date>1998-05</date><risdate>1998</risdate><volume>8</volume><issue>2</issue><spage>440</spage><epage>446</epage><pages>440-446</pages><issn>1051-0761</issn><eissn>1939-5582</eissn><abstract>In a northwestern Connecticut forest, we quantified the carbon (C) and nitrogen (N) content of the forest floor and the top 15 cm of mineral soil and the rate of midsummer net N mineralization beneath six different tree species. There were large interspecific differences in forest floor depth and mass, in the size and distribution of C and N pools at varying soil depths, and in rates of midsummer net N mineralization and nitrification. Forest floor mass ranged from 3.2 kg/m2to 11.0 kg/m2and was smallest beneath sugar maple and largest beneath hemlock. The pool size of C in the forest floor ranged from 1.1 kg/m2to 4.4 kg/m2while the N content of the forest floor ranged from 83 g/m2to 229 g/m2. Forest floor C and N pools were smallest beneath sugar maple and highest beneath hemlock. Soil C:N ratios (range: 14.8-19.5) were lower beneath sugar maple, red maple, and white ash than beneath beech, red oak, and hemlock, whereas the opposite was true of the midsummer rate of net N mineralization (range: 0.91-2.02 g·m-2·28 d-1). The rate of net nitrification was positively correlated with the rate of net N mineralization. Interspecific differences in litter production and quality explain the large differences among species in the size of the forest floor C and N pools and in net N mineralization rates. The differences in the size and distribution of C and N pools beneath the different species suggest that the mechanisms regulating the process of species replacement in these forests will mediate the effects of anthropogenic, environmental changes in soil C and N dynamics.</abstract><pub>Ecological Society of America</pub><doi>10.1890/1051-0761(1998)008[0440:ctsiwt]2.0.co;2</doi><tpages>7</tpages></addata></record>
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ispartof Ecological applications, 1998-05, Vol.8 (2), p.440-446
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1939-5582
language eng
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source Wiley; JSTOR Archival Journals and Primary Sources Collection
subjects carbon
Coniferous forests
ecosystem
forest
Forest ecology
Forest litter
Forest soils
Maple sugar
Mineral soils
Nitrification
Nitrogen
Soil ecology
soils, forest
Trees
title Canopy Tree-Soil Interactions within Temperate Forests: Species Effects on Soil Carbon and Nitrogen
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