Atmospheric deposition and canopy interactions of nitrogen in forests

Wet deposition of nitrogen compounds was measured and dry and cloud water deposition were estimated at 11 forested sites in North America and one site in Europe. Dry deposition was a significant pathway of N input to all the forests, averaging 46% of the total deposition. At most of these sites, NH4...

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Veröffentlicht in:Canadian journal of forest research 1993-08, Vol.23 (8), p.1603-1616
Hauptverfasser: Lovett, G.M, Lindberg, S.E
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Lindberg, S.E
description Wet deposition of nitrogen compounds was measured and dry and cloud water deposition were estimated at 11 forested sites in North America and one site in Europe. Dry deposition was a significant pathway of N input to all the forests, averaging 46% of the total deposition. At most of these sites, NH4+ was the dominant form of fixed N in the air, but HNO3 vapor dominated the dry deposition of N. Coarse-particle deposition was often important, but fine-particle deposition usually contributed only a small amount of the dry-deposited N. The deposition rates of inorganic N, which ranged between 4.8 and 27 kg N ha(-1) year(-1), were generally much higher than has been reported by other studies measuring only wet or bulk deposition. The highest deposition rates were at the high-elevation sites in the southeastern and northeastern United States and much of the deposition at these sites was attributed to cloud water. Throughfall and stemflow (TF + SF) flux was also measured at all sites, and the net canopy exchange (NCE = (TF + SF) - total deposition) was found to be negative (indicating consumption of NO(3-) in the canopy) for and positive (indicating canopy release) for organic N. Past reports of canopy release of Can probably be attributed to washoff of dry-deposited NO(3-) species. Consumption of inorganic N in the canopy ranged from 1 to 12 kg N.ha(-1). year(-1), and was highest in the spruce and spruce-fir stands. When organic N was included in the canopy N balance, the net canopy uptake of N was generally 15% of the total system N requirement. Total N deposition was a linear function of wet deposition for low-elevation sites, and dry deposition was a linear function of the net throughfall flux for NO(-)3
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Dry deposition was a significant pathway of N input to all the forests, averaging 46% of the total deposition. At most of these sites, NH4+ was the dominant form of fixed N in the air, but HNO3 vapor dominated the dry deposition of N. Coarse-particle deposition was often important, but fine-particle deposition usually contributed only a small amount of the dry-deposited N. The deposition rates of inorganic N, which ranged between 4.8 and 27 kg N ha(-1) year(-1), were generally much higher than has been reported by other studies measuring only wet or bulk deposition. The highest deposition rates were at the high-elevation sites in the southeastern and northeastern United States and much of the deposition at these sites was attributed to cloud water. Throughfall and stemflow (TF + SF) flux was also measured at all sites, and the net canopy exchange (NCE = (TF + SF) - total deposition) was found to be negative (indicating consumption of NO(3-) in the canopy) for and positive (indicating canopy release) for organic N. Past reports of canopy release of Can probably be attributed to washoff of dry-deposited NO(3-) species. Consumption of inorganic N in the canopy ranged from 1 to 12 kg N.ha(-1). year(-1), and was highest in the spruce and spruce-fir stands. When organic N was included in the canopy N balance, the net canopy uptake of N was generally 15% of the total system N requirement. 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Dry deposition was a significant pathway of N input to all the forests, averaging 46% of the total deposition. At most of these sites, NH4+ was the dominant form of fixed N in the air, but HNO3 vapor dominated the dry deposition of N. Coarse-particle deposition was often important, but fine-particle deposition usually contributed only a small amount of the dry-deposited N. The deposition rates of inorganic N, which ranged between 4.8 and 27 kg N ha(-1) year(-1), were generally much higher than has been reported by other studies measuring only wet or bulk deposition. The highest deposition rates were at the high-elevation sites in the southeastern and northeastern United States and much of the deposition at these sites was attributed to cloud water. 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General forest ecology</topic><topic>MOUVEMENT</topic><topic>MOVIMIENTO</topic><topic>NITROGENO</topic><topic>PRECIPITACION ATMOSFERICA</topic><topic>PRECIPITATION</topic><topic>PRODUCTOS QUIMICOS</topic><topic>PRODUIT CHIMIQUE</topic><topic>Synecology</topic><topic>Terrestrial ecosystems</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Lovett, G.M</creatorcontrib><creatorcontrib>Lindberg, S.E</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><jtitle>Canadian journal of forest research</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Lovett, G.M</au><au>Lindberg, S.E</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Atmospheric deposition and canopy interactions of nitrogen in forests</atitle><jtitle>Canadian journal of forest research</jtitle><addtitle>Revue canadienne de recherche forestière</addtitle><date>1993-08-01</date><risdate>1993</risdate><volume>23</volume><issue>8</issue><spage>1603</spage><epage>1616</epage><pages>1603-1616</pages><issn>0045-5067</issn><eissn>1208-6037</eissn><coden>CJFRAR</coden><abstract>Wet deposition of nitrogen compounds was measured and dry and cloud water deposition were estimated at 11 forested sites in North America and one site in Europe. Dry deposition was a significant pathway of N input to all the forests, averaging 46% of the total deposition. At most of these sites, NH4+ was the dominant form of fixed N in the air, but HNO3 vapor dominated the dry deposition of N. Coarse-particle deposition was often important, but fine-particle deposition usually contributed only a small amount of the dry-deposited N. The deposition rates of inorganic N, which ranged between 4.8 and 27 kg N ha(-1) year(-1), were generally much higher than has been reported by other studies measuring only wet or bulk deposition. The highest deposition rates were at the high-elevation sites in the southeastern and northeastern United States and much of the deposition at these sites was attributed to cloud water. 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subjects Agronomy. Soil science and plant productions
ALTITUD
ALTITUDE
AMERICA DEL NORTE
AMERIQUE DU NORD
Animal and plant ecology
Animal, plant and microbial ecology
AZOTE
Biological and medical sciences
BOSQUES
COUVERT
CUBIERTA DE COPAS
ECOSISTEMA
ECOSYSTEME
EUROPA
EUROPE
Forestry
FORET
Fundamental and applied biological sciences. Psychology
General forest ecology
Generalities. Production, biomass. Quality of wood and forest products. General forest ecology
MOUVEMENT
MOVIMIENTO
NITROGENO
PRECIPITACION ATMOSFERICA
PRECIPITATION
PRODUCTOS QUIMICOS
PRODUIT CHIMIQUE
Synecology
Terrestrial ecosystems
title Atmospheric deposition and canopy interactions of nitrogen in forests
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