CheneBelgiqueV2, PascalFrancis, Corpus, bibRecord, 000133

Transpiration from a multi-species deciduous forest as estimated by xylem sap flow techniques

Identifieur interne : 000133 ( PascalFrancis/Corpus ); précédent : 000132; suivant : 000134

Transpiration from a multi-species deciduous forest as estimated by xylem sap flow techniques

Auteurs : Stan D. Wullschleger ; P. J. Hanson ; D. E. Todd

Source :

Forest ecology and management [ 0378-1127 ] ; 2001.

RBID : Pascal:01-0203679

Descripteurs français

Pascal (Inist)
- Modèle prévision, Estimation, Evapotranspiration, Peuplement forestier mélangé, Xylème, Sève, Bassin versant, Hydrologie, Comparaison interspécifique, Quercus alba, Quercus rubra, Acer rubrum, Liriodendron tulipifera, Tennessee, Composition floristique, Ressource eau, Nyssa sylvatica, Quercus prinus.

English descriptors

KwdEn :
- Acer rubrum, Estimation, Evapotranspiration, Floristic composition, Forecast model, Hydrology, Interspecific comparison, Liriodendron tulipifera, Mixed forest stand, Quercus alba, Quercus rubra, Sap, Tennessee, Water resources, Watershed, Xylem.

Abstract

Thermal dissipation probes inserted into hydro-active sapwood were used to measure rates of xylem sap flow for six major hardwood species growing in an upland oak forest of east TN. Species-specific estimates of sap flow were combined with total sapwood area for trees of the forest overstory and understory, and daily rates of stand transpiration were derived. A seasonal analysis of sap flow for nine chestnut oak (Quercus prinus L.) trees measured in 1996 showed that radiation, vapor pressure deficit, and fractional leaf area index (LAI) were sufficient to describe rates of daily transpiration. Application of an empirical model to climatic data collected in 1997 and maximum daily rates of sap flow for white oak (Quercus alba L.), northern red oak (Quercus rubra L.), black gum (Nyssa sylvatica Marsh.), red maple (Acer rubrum L.), and yellow-poplar (Liriodendron tulipifera L.) indicated that stand transpiration peaked at 2.2 mm day^-1 in mid-May prior to canopy closure. Total transpiration during the season was 267 mm: 221 mm from overstory trees and 46 mm from understory saplings. Transpiration from the overstory was dominated by red maple (59 mm) and black gum (49 mm). Chestnut oak, which accounted for 27% of the stand basal area, contributed only 35 mm or 16% to total overstory transpiration. The relative contribution of each species to stand transpiration was driven largely by sapwood area per unit ground area and to a lesser extent by species-specific differences in daily water use. Such information should prove useful in exploring the impact of harvest operations on site water balance and in understanding the ecologica basis for how species composition affects forest water use.

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

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A03		`1`		`@0 For. ecol. manage.`
A05				`@2 143`
A06				`@2 1-3`
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A09	`01`	`1`	`ENG`	`@1 The Science of Managing Forests to Sustain Water Resources`
A11	`01`	`1`		`@1 WULLSCHLEGER (Stan D.)`
A11	`02`	`1`		`@1 HANSON (P. J.)`
A11	`03`	`1`		`@1 TODD (D. E.)`
A12	`01`	`1`		`@1 BROOKS (Robert T.) @9 ed.`
A12	`02`	`1`		`@1 LUST (Noël) @9 ed.`
A14	`01`			`@1 Environmental Sciences Division, Oak Ridge National Laboratory @2 Oak Ridge, TN 37831-6422 @3 USA @Z 1 aut. @Z 2 aut. @Z 3 aut.`
A15	`01`			`@1 USDA Forest Service, Northeastern Research Station @2 Amherst, Massachusetts, 01003 @3 USA @Z 1 aut.`
A15	`02`			`@1 University of Ghent, Laboratory of Forestry @2 9090 Gontrode @3 BEL @Z 2 aut.`
A20				`@1 205-213`
A21				`@1 2001`
A23	`01`			`@0 ENG`
A43	`01`			`@1 INIST @2 17223 @5 354000094581190190`
A44				`@0 0000 @1 © 2001 INIST-CNRS. All rights reserved.`
A45				`@0 24 ref.`
A47	`01`	`1`		`@0 01-0203679`
A60				`@1 P @2 C`
A61				`@0 A`
A64	`01`	`1`		`@0 Forest ecology and management`
A66	`01`			`@0 NLD`
C01	`01`		`ENG`	@0 Thermal dissipation probes inserted into hydro-active sapwood were used to measure rates of xylem sap flow for six major hardwood species growing in an upland oak forest of east TN. Species-specific estimates of sap flow were combined with total sapwood area for trees of the forest overstory and understory, and daily rates of stand transpiration were derived. A seasonal analysis of sap flow for nine chestnut oak (Quercus prinus L.) trees measured in 1996 showed that radiation, vapor pressure deficit, and fractional leaf area index (LAI) were sufficient to describe rates of daily transpiration. Application of an empirical model to climatic data collected in 1997 and maximum daily rates of sap flow for white oak (Quercus alba L.), northern red oak (Quercus rubra L.), black gum (Nyssa sylvatica Marsh.), red maple (Acer rubrum L.), and yellow-poplar (Liriodendron tulipifera L.) indicated that stand transpiration peaked at 2.2 mm day^-1 in mid-May prior to canopy closure. Total transpiration during the season was 267 mm: 221 mm from overstory trees and 46 mm from understory saplings. Transpiration from the overstory was dominated by red maple (59 mm) and black gum (49 mm). Chestnut oak, which accounted for 27% of the stand basal area, contributed only 35 mm or 16% to total overstory transpiration. The relative contribution of each species to stand transpiration was driven largely by sapwood area per unit ground area and to a lesser extent by species-specific differences in daily water use. Such information should prove useful in exploring the impact of harvest operations on site water balance and in understanding the ecologica basis for how species composition affects forest water use.
C02	`01`	`X`		`@0 002A33C01`
C02	`02`	`X`		`@0 001E01N03`
C02	`03`	`2`		`@0 226A03`
C03	`01`	`X`	`FRE`	`@0 Modèle prévision @5 01`
C03	`01`	`X`	`ENG`	`@0 Forecast model @5 01`
C03	`01`	`X`	`SPA`	`@0 Modelo previsión @5 01`
C03	`02`	`X`	`FRE`	`@0 Estimation @5 02`
C03	`02`	`X`	`ENG`	`@0 Estimation @5 02`
C03	`02`	`X`	`SPA`	`@0 Estimación @5 02`
C03	`03`	`X`	`FRE`	`@0 Evapotranspiration @5 03`
C03	`03`	`X`	`ENG`	`@0 Evapotranspiration @5 03`
C03	`03`	`X`	`SPA`	`@0 Evapotranspiración @5 03`
C03	`04`	`X`	`FRE`	`@0 Peuplement forestier mélangé @5 04`
C03	`04`	`X`	`ENG`	`@0 Mixed forest stand @5 04`
C03	`04`	`X`	`SPA`	`@0 Rodal forestal mixto @5 04`
C03	`05`	`X`	`FRE`	`@0 Xylème @5 05`
C03	`05`	`X`	`ENG`	`@0 Xylem @5 05`
C03	`05`	`X`	`SPA`	`@0 Xilema @5 05`
C03	`06`	`X`	`FRE`	`@0 Sève @5 06`
C03	`06`	`X`	`ENG`	`@0 Sap @5 06`
C03	`06`	`X`	`SPA`	`@0 Savia @5 06`
C03	`07`	`X`	`FRE`	`@0 Bassin versant @5 07`
C03	`07`	`X`	`ENG`	`@0 Watershed @5 07`
C03	`07`	`X`	`SPA`	`@0 Cuenca @5 07`
C03	`08`	`X`	`FRE`	`@0 Hydrologie @5 08`
C03	`08`	`X`	`ENG`	`@0 Hydrology @5 08`
C03	`08`	`X`	`SPA`	`@0 Hidrología @5 08`
C03	`09`	`X`	`FRE`	`@0 Comparaison interspécifique @5 09`
C03	`09`	`X`	`ENG`	`@0 Interspecific comparison @5 09`
C03	`09`	`X`	`SPA`	`@0 Comparación interespecífica @5 09`
C03	`10`	`X`	`FRE`	`@0 Quercus alba @2 NS @5 11`
C03	`10`	`X`	`ENG`	`@0 Quercus alba @2 NS @5 11`
C03	`10`	`X`	`SPA`	`@0 Quercus alba @2 NS @5 11`
C03	`11`	`X`	`FRE`	`@0 Quercus rubra @2 NS @5 12`
C03	`11`	`X`	`ENG`	`@0 Quercus rubra @2 NS @5 12`
C03	`11`	`X`	`SPA`	`@0 Quercus rubra @2 NS @5 12`
C03	`12`	`X`	`FRE`	`@0 Acer rubrum @2 NS @5 13`
C03	`12`	`X`	`ENG`	`@0 Acer rubrum @2 NS @5 13`
C03	`12`	`X`	`SPA`	`@0 Acer rubrum @2 NS @5 13`
C03	`13`	`X`	`FRE`	`@0 Liriodendron tulipifera @2 NS @5 14`
C03	`13`	`X`	`ENG`	`@0 Liriodendron tulipifera @2 NS @5 14`
C03	`13`	`X`	`SPA`	`@0 Liriodendron tulipifera @2 NS @5 14`
C03	`14`	`X`	`FRE`	`@0 Tennessee @2 NG @5 20`
C03	`14`	`X`	`ENG`	`@0 Tennessee @2 NG @5 20`
C03	`14`	`X`	`SPA`	`@0 Tennessee @2 NG @5 20`
C03	`15`	`X`	`FRE`	`@0 Composition floristique @5 33`
C03	`15`	`X`	`ENG`	`@0 Floristic composition @5 33`
C03	`15`	`X`	`SPA`	`@0 Composición florística @5 33`
C03	`16`	`X`	`FRE`	`@0 Ressource eau @5 34`
C03	`16`	`X`	`ENG`	`@0 Water resources @5 34`
C03	`16`	`X`	`SPA`	`@0 Recurso agua @5 34`
C03	`17`	`X`	`FRE`	`@0 Nyssa sylvatica @2 NS @4 INC @5 76`
C03	`18`	`X`	`FRE`	`@0 Quercus prinus @2 NS @4 INC @5 77`
C07	`01`	`X`	`FRE`	`@0 Fagaceae @2 NS`
C07	`01`	`X`	`ENG`	`@0 Fagaceae @2 NS`
C07	`01`	`X`	`SPA`	`@0 Fagaceae @2 NS`
C07	`02`	`X`	`FRE`	`@0 Dicotyledones @2 NS`
C07	`02`	`X`	`ENG`	`@0 Dicotyledones @2 NS`
C07	`02`	`X`	`SPA`	`@0 Dicotyledones @2 NS`
C07	`03`	`X`	`FRE`	`@0 Angiospermae @2 NS`
C07	`03`	`X`	`ENG`	`@0 Angiospermae @2 NS`
C07	`03`	`X`	`SPA`	`@0 Angiospermae @2 NS`
C07	`04`	`X`	`FRE`	`@0 Spermatophyta @2 NS`
C07	`04`	`X`	`ENG`	`@0 Spermatophyta @2 NS`
C07	`04`	`X`	`SPA`	`@0 Spermatophyta @2 NS`
C07	`05`	`X`	`FRE`	`@0 Aceraceae @2 NS`
C07	`05`	`X`	`ENG`	`@0 Aceraceae @2 NS`
C07	`05`	`X`	`SPA`	`@0 Aceraceae @2 NS`
C07	`06`	`X`	`FRE`	`@0 Magnoliaceae @2 NS`
C07	`06`	`X`	`ENG`	`@0 Magnoliaceae @2 NS`
C07	`06`	`X`	`SPA`	`@0 Magnoliaceae @2 NS`
C07	`07`	`X`	`FRE`	`@0 Etats Unis @2 NG`
C07	`07`	`X`	`ENG`	`@0 United States @2 NG`
C07	`07`	`X`	`SPA`	`@0 Estados Unidos @2 NG`
C07	`08`	`X`	`FRE`	`@0 Amérique du Nord @2 NG`
C07	`08`	`X`	`ENG`	`@0 North America @2 NG`
C07	`08`	`X`	`SPA`	`@0 America del norte @2 NG`
C07	`09`	`X`	`FRE`	`@0 Amérique @2 NG`
C07	`09`	`X`	`ENG`	`@0 America @2 NG`
C07	`09`	`X`	`SPA`	`@0 America @2 NG`
C07	`10`	`X`	`FRE`	`@0 Arbre forestier feuillu @5 40`
C07	`10`	`X`	`ENG`	`@0 Hardwood forest tree @5 40`
C07	`10`	`X`	`SPA`	`@0 Arbol forestal frondoso @5 40`
C07	`11`	`X`	`FRE`	`@0 Nyssaceae @2 NS @5 47`
C07	`11`	`X`	`ENG`	`@0 Nyssaceae @2 NS @5 47`
C07	`11`	`X`	`SPA`	`@0 Nyssaceae @2 NS @5 47`
N21				`@1 141`

A30	`01`	`1`	`ENG`	`@1 The Science of Managing Forests to Sustain Water Resources. International Conference @3 Sturbridge, Massachusetts USA @4 1998-11-08`

Format Inist (serveur)

NO :	PASCAL 01-0203679 INIST
ET :	Transpiration from a multi-species deciduous forest as estimated by xylem sap flow techniques
AU :	WULLSCHLEGER (Stan D.); HANSON (P. J.); TODD (D. E.); BROOKS (Robert T.); LUST (Noël)
AF :	Environmental Sciences Division, Oak Ridge National Laboratory/Oak Ridge, TN 37831-6422/Etats-Unis (1 aut., 2 aut., 3 aut.); USDA Forest Service, Northeastern Research Station/Amherst, Massachusetts, 01003/Etats-Unis (1 aut.); University of Ghent, Laboratory of Forestry/9090 Gontrode/Belgique (2 aut.)
DT :	Publication en série; Congrès; Niveau analytique
SO :	Forest ecology and management; ISSN 0378-1127; Coden FECMDW; Pays-Bas; Da. 2001; Vol. 143; No. 1-3; Pp. 205-213; Bibl. 24 ref.
LA :	Anglais
EA :	Thermal dissipation probes inserted into hydro-active sapwood were used to measure rates of xylem sap flow for six major hardwood species growing in an upland oak forest of east TN. Species-specific estimates of sap flow were combined with total sapwood area for trees of the forest overstory and understory, and daily rates of stand transpiration were derived. A seasonal analysis of sap flow for nine chestnut oak (Quercus prinus L.) trees measured in 1996 showed that radiation, vapor pressure deficit, and fractional leaf area index (LAI) were sufficient to describe rates of daily transpiration. Application of an empirical model to climatic data collected in 1997 and maximum daily rates of sap flow for white oak (Quercus alba L.), northern red oak (Quercus rubra L.), black gum (Nyssa sylvatica Marsh.), red maple (Acer rubrum L.), and yellow-poplar (Liriodendron tulipifera L.) indicated that stand transpiration peaked at 2.2 mm day^-1 in mid-May prior to canopy closure. Total transpiration during the season was 267 mm: 221 mm from overstory trees and 46 mm from understory saplings. Transpiration from the overstory was dominated by red maple (59 mm) and black gum (49 mm). Chestnut oak, which accounted for 27% of the stand basal area, contributed only 35 mm or 16% to total overstory transpiration. The relative contribution of each species to stand transpiration was driven largely by sapwood area per unit ground area and to a lesser extent by species-specific differences in daily water use. Such information should prove useful in exploring the impact of harvest operations on site water balance and in understanding the ecologica basis for how species composition affects forest water use.
CC :	002A33C01; 001E01N03; 226A03
FD :	Modèle prévision; Estimation; Evapotranspiration; Peuplement forestier mélangé; Xylème; Sève; Bassin versant; Hydrologie; Comparaison interspécifique; Quercus alba; Quercus rubra; Acer rubrum; Liriodendron tulipifera; Tennessee; Composition floristique; Ressource eau; Nyssa sylvatica; Quercus prinus
FG :	Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Aceraceae; Magnoliaceae; Etats Unis; Amérique du Nord; Amérique; Arbre forestier feuillu; Nyssaceae
ED :	Forecast model; Estimation; Evapotranspiration; Mixed forest stand; Xylem; Sap; Watershed; Hydrology; Interspecific comparison; Quercus alba; Quercus rubra; Acer rubrum; Liriodendron tulipifera; Tennessee; Floristic composition; Water resources
EG :	Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Aceraceae; Magnoliaceae; United States; North America; America; Hardwood forest tree; Nyssaceae
SD :	Modelo previsión; Estimación; Evapotranspiración; Rodal forestal mixto; Xilema; Savia; Cuenca; Hidrología; Comparación interespecífica; Quercus alba; Quercus rubra; Acer rubrum; Liriodendron tulipifera; Tennessee; Composición florística; Recurso agua
LO :	INIST-17223.354000094581190190
ID :	01-0203679

Links to Exploration step

Pascal:01-0203679

Le document en format XML

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<term>Hydrology</term>
<term>Interspecific comparison</term>
<term>Liriodendron tulipifera</term>
<term>Mixed forest stand</term>
<term>Quercus alba</term>
<term>Quercus rubra</term>
<term>Sap</term>
<term>Tennessee</term>
<term>Water resources</term>
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</keywords>
<keywords scheme="Pascal" xml:lang="fr"><term>Modèle prévision</term>
<term>Estimation</term>
<term>Evapotranspiration</term>
<term>Peuplement forestier mélangé</term>
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<term>Sève</term>
<term>Bassin versant</term>
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<front><div type="abstract" xml:lang="en">Thermal dissipation probes inserted into hydro-active sapwood were used to measure rates of xylem sap flow for six major hardwood species growing in an upland oak forest of east TN. Species-specific estimates of sap flow were combined with total sapwood area for trees of the forest overstory and understory, and daily rates of stand transpiration were derived. A seasonal analysis of sap flow for nine chestnut oak (Quercus prinus L.) trees measured in 1996 showed that radiation, vapor pressure deficit, and fractional leaf area index (LAI) were sufficient to describe rates of daily transpiration. Application of an empirical model to climatic data collected in 1997 and maximum daily rates of sap flow for white oak (Quercus alba L.), northern red oak (Quercus rubra L.), black gum (Nyssa sylvatica Marsh.), red maple (Acer rubrum L.), and yellow-poplar (Liriodendron tulipifera L.) indicated that stand transpiration peaked at 2.2 mm day<sup>-1</sup>
 in mid-May prior to canopy closure. Total transpiration during the season was 267 mm: 221 mm from overstory trees and 46 mm from understory saplings. Transpiration from the overstory was dominated by red maple (59 mm) and black gum (49 mm). Chestnut oak, which accounted for 27% of the stand basal area, contributed only 35 mm or 16% to total overstory transpiration. The relative contribution of each species to stand transpiration was driven largely by sapwood area per unit ground area and to a lesser extent by species-specific differences in daily water use. Such information should prove useful in exploring the impact of harvest operations on site water balance and in understanding the ecologica basis for how species composition affects forest water use.</div>
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</fA11>
<fA11 i1="02" i2="1"><s1>HANSON (P. J.)</s1>
</fA11>
<fA11 i1="03" i2="1"><s1>TODD (D. E.)</s1>
</fA11>
<fA12 i1="01" i2="1"><s1>BROOKS (Robert T.)</s1>
<s9>ed.</s9>
</fA12>
<fA12 i1="02" i2="1"><s1>LUST (Noël)</s1>
<s9>ed.</s9>
</fA12>
<fA14 i1="01"><s1>Environmental Sciences Division, Oak Ridge National Laboratory</s1>
<s2>Oak Ridge, TN 37831-6422</s2>
<s3>USA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>3 aut.</sZ>
</fA14>
<fA15 i1="01"><s1>USDA Forest Service, Northeastern Research Station</s1>
<s2>Amherst, Massachusetts, 01003</s2>
<s3>USA</s3>
<sZ>1 aut.</sZ>
</fA15>
<fA15 i1="02"><s1>University of Ghent, Laboratory of Forestry</s1>
<s2>9090 Gontrode</s2>
<s3>BEL</s3>
<sZ>2 aut.</sZ>
</fA15>
<fA20><s1>205-213</s1>
</fA20>
<fA21><s1>2001</s1>
</fA21>
<fA23 i1="01"><s0>ENG</s0>
</fA23>
<fA43 i1="01"><s1>INIST</s1>
<s2>17223</s2>
<s5>354000094581190190</s5>
</fA43>
<fA44><s0>0000</s0>
<s1>© 2001 INIST-CNRS. All rights reserved.</s1>
</fA44>
<fA45><s0>24 ref.</s0>
</fA45>
<fA47 i1="01" i2="1"><s0>01-0203679</s0>
</fA47>
<fA60><s1>P</s1>
<s2>C</s2>
</fA60>
<fA61><s0>A</s0>
</fA61>
<fA64 i1="01" i2="1"><s0>Forest ecology and management</s0>
</fA64>
<fA66 i1="01"><s0>NLD</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>Thermal dissipation probes inserted into hydro-active sapwood were used to measure rates of xylem sap flow for six major hardwood species growing in an upland oak forest of east TN. Species-specific estimates of sap flow were combined with total sapwood area for trees of the forest overstory and understory, and daily rates of stand transpiration were derived. A seasonal analysis of sap flow for nine chestnut oak (Quercus prinus L.) trees measured in 1996 showed that radiation, vapor pressure deficit, and fractional leaf area index (LAI) were sufficient to describe rates of daily transpiration. Application of an empirical model to climatic data collected in 1997 and maximum daily rates of sap flow for white oak (Quercus alba L.), northern red oak (Quercus rubra L.), black gum (Nyssa sylvatica Marsh.), red maple (Acer rubrum L.), and yellow-poplar (Liriodendron tulipifera L.) indicated that stand transpiration peaked at 2.2 mm day<sup>-1</sup>
 in mid-May prior to canopy closure. Total transpiration during the season was 267 mm: 221 mm from overstory trees and 46 mm from understory saplings. Transpiration from the overstory was dominated by red maple (59 mm) and black gum (49 mm). Chestnut oak, which accounted for 27% of the stand basal area, contributed only 35 mm or 16% to total overstory transpiration. The relative contribution of each species to stand transpiration was driven largely by sapwood area per unit ground area and to a lesser extent by species-specific differences in daily water use. Such information should prove useful in exploring the impact of harvest operations on site water balance and in understanding the ecologica basis for how species composition affects forest water use.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>002A33C01</s0>
</fC02>
<fC02 i1="02" i2="X"><s0>001E01N03</s0>
</fC02>
<fC02 i1="03" i2="2"><s0>226A03</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Modèle prévision</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Forecast model</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Modelo previsión</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Estimation</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Estimation</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Estimación</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Evapotranspiration</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Evapotranspiration</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Evapotranspiración</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Peuplement forestier mélangé</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Mixed forest stand</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Rodal forestal mixto</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Xylème</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Xylem</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Xilema</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Sève</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Sap</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Savia</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Bassin versant</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Watershed</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Cuenca</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Hydrologie</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Hydrology</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Hidrología</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Comparaison interspécifique</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Interspecific comparison</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Comparación interespecífica</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Quercus alba</s0>
<s2>NS</s2>
<s5>11</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Quercus alba</s0>
<s2>NS</s2>
<s5>11</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Quercus alba</s0>
<s2>NS</s2>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Quercus rubra</s0>
<s2>NS</s2>
<s5>12</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Quercus rubra</s0>
<s2>NS</s2>
<s5>12</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Quercus rubra</s0>
<s2>NS</s2>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Acer rubrum</s0>
<s2>NS</s2>
<s5>13</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Acer rubrum</s0>
<s2>NS</s2>
<s5>13</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Acer rubrum</s0>
<s2>NS</s2>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Liriodendron tulipifera</s0>
<s2>NS</s2>
<s5>14</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG"><s0>Liriodendron tulipifera</s0>
<s2>NS</s2>
<s5>14</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA"><s0>Liriodendron tulipifera</s0>
<s2>NS</s2>
<s5>14</s5>
</fC03>
<fC03 i1="14" i2="X" l="FRE"><s0>Tennessee</s0>
<s2>NG</s2>
<s5>20</s5>
</fC03>
<fC03 i1="14" i2="X" l="ENG"><s0>Tennessee</s0>
<s2>NG</s2>
<s5>20</s5>
</fC03>
<fC03 i1="14" i2="X" l="SPA"><s0>Tennessee</s0>
<s2>NG</s2>
<s5>20</s5>
</fC03>
<fC03 i1="15" i2="X" l="FRE"><s0>Composition floristique</s0>
<s5>33</s5>
</fC03>
<fC03 i1="15" i2="X" l="ENG"><s0>Floristic composition</s0>
<s5>33</s5>
</fC03>
<fC03 i1="15" i2="X" l="SPA"><s0>Composición florística</s0>
<s5>33</s5>
</fC03>
<fC03 i1="16" i2="X" l="FRE"><s0>Ressource eau</s0>
<s5>34</s5>
</fC03>
<fC03 i1="16" i2="X" l="ENG"><s0>Water resources</s0>
<s5>34</s5>
</fC03>
<fC03 i1="16" i2="X" l="SPA"><s0>Recurso agua</s0>
<s5>34</s5>
</fC03>
<fC03 i1="17" i2="X" l="FRE"><s0>Nyssa sylvatica</s0>
<s2>NS</s2>
<s4>INC</s4>
<s5>76</s5>
</fC03>
<fC03 i1="18" i2="X" l="FRE"><s0>Quercus prinus</s0>
<s2>NS</s2>
<s4>INC</s4>
<s5>77</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE"><s0>Fagaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG"><s0>Fagaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA"><s0>Fagaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="ENG"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="02" i2="X" l="SPA"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="FRE"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="ENG"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="SPA"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="FRE"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="ENG"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="SPA"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="FRE"><s0>Aceraceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="ENG"><s0>Aceraceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="SPA"><s0>Aceraceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="FRE"><s0>Magnoliaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="ENG"><s0>Magnoliaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="SPA"><s0>Magnoliaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="FRE"><s0>Etats Unis</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="07" i2="X" l="ENG"><s0>United States</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="07" i2="X" l="SPA"><s0>Estados Unidos</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="08" i2="X" l="FRE"><s0>Amérique du Nord</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="08" i2="X" l="ENG"><s0>North America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="08" i2="X" l="SPA"><s0>America del norte</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="09" i2="X" l="FRE"><s0>Amérique</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="09" i2="X" l="ENG"><s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="09" i2="X" l="SPA"><s0>America</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="10" i2="X" l="FRE"><s0>Arbre forestier feuillu</s0>
<s5>40</s5>
</fC07>
<fC07 i1="10" i2="X" l="ENG"><s0>Hardwood forest tree</s0>
<s5>40</s5>
</fC07>
<fC07 i1="10" i2="X" l="SPA"><s0>Arbol forestal frondoso</s0>
<s5>40</s5>
</fC07>
<fC07 i1="11" i2="X" l="FRE"><s0>Nyssaceae</s0>
<s2>NS</s2>
<s5>47</s5>
</fC07>
<fC07 i1="11" i2="X" l="ENG"><s0>Nyssaceae</s0>
<s2>NS</s2>
<s5>47</s5>
</fC07>
<fC07 i1="11" i2="X" l="SPA"><s0>Nyssaceae</s0>
<s2>NS</s2>
<s5>47</s5>
</fC07>
<fN21><s1>141</s1>
</fN21>
</pA>
<pR><fA30 i1="01" i2="1" l="ENG"><s1>The Science of Managing Forests to Sustain Water Resources. International Conference</s1>
<s3>Sturbridge, Massachusetts USA</s3>
<s4>1998-11-08</s4>
</fA30>
</pR>
</standard>
<server><NO>PASCAL 01-0203679 INIST</NO>
<ET>Transpiration from a multi-species deciduous forest as estimated by xylem sap flow techniques</ET>
<AU>WULLSCHLEGER (Stan D.); HANSON (P. J.); TODD (D. E.); BROOKS (Robert T.); LUST (Noël)</AU>
<AF>Environmental Sciences Division, Oak Ridge National Laboratory/Oak Ridge, TN 37831-6422/Etats-Unis (1 aut., 2 aut., 3 aut.); USDA Forest Service, Northeastern Research Station/Amherst, Massachusetts, 01003/Etats-Unis (1 aut.); University of Ghent, Laboratory of Forestry/9090 Gontrode/Belgique (2 aut.)</AF>
<DT>Publication en série; Congrès; Niveau analytique</DT>
<SO>Forest ecology and management; ISSN 0378-1127; Coden FECMDW; Pays-Bas; Da. 2001; Vol. 143; No. 1-3; Pp. 205-213; Bibl. 24 ref.</SO>
<LA>Anglais</LA>
<EA>Thermal dissipation probes inserted into hydro-active sapwood were used to measure rates of xylem sap flow for six major hardwood species growing in an upland oak forest of east TN. Species-specific estimates of sap flow were combined with total sapwood area for trees of the forest overstory and understory, and daily rates of stand transpiration were derived. A seasonal analysis of sap flow for nine chestnut oak (Quercus prinus L.) trees measured in 1996 showed that radiation, vapor pressure deficit, and fractional leaf area index (LAI) were sufficient to describe rates of daily transpiration. Application of an empirical model to climatic data collected in 1997 and maximum daily rates of sap flow for white oak (Quercus alba L.), northern red oak (Quercus rubra L.), black gum (Nyssa sylvatica Marsh.), red maple (Acer rubrum L.), and yellow-poplar (Liriodendron tulipifera L.) indicated that stand transpiration peaked at 2.2 mm day<sup>-1</sup>
 in mid-May prior to canopy closure. Total transpiration during the season was 267 mm: 221 mm from overstory trees and 46 mm from understory saplings. Transpiration from the overstory was dominated by red maple (59 mm) and black gum (49 mm). Chestnut oak, which accounted for 27% of the stand basal area, contributed only 35 mm or 16% to total overstory transpiration. The relative contribution of each species to stand transpiration was driven largely by sapwood area per unit ground area and to a lesser extent by species-specific differences in daily water use. Such information should prove useful in exploring the impact of harvest operations on site water balance and in understanding the ecologica basis for how species composition affects forest water use.</EA>
<CC>002A33C01; 001E01N03; 226A03</CC>
<FD>Modèle prévision; Estimation; Evapotranspiration; Peuplement forestier mélangé; Xylème; Sève; Bassin versant; Hydrologie; Comparaison interspécifique; Quercus alba; Quercus rubra; Acer rubrum; Liriodendron tulipifera; Tennessee; Composition floristique; Ressource eau; Nyssa sylvatica; Quercus prinus</FD>
<FG>Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Aceraceae; Magnoliaceae; Etats Unis; Amérique du Nord; Amérique; Arbre forestier feuillu; Nyssaceae</FG>
<ED>Forecast model; Estimation; Evapotranspiration; Mixed forest stand; Xylem; Sap; Watershed; Hydrology; Interspecific comparison; Quercus alba; Quercus rubra; Acer rubrum; Liriodendron tulipifera; Tennessee; Floristic composition; Water resources</ED>
<EG>Fagaceae; Dicotyledones; Angiospermae; Spermatophyta; Aceraceae; Magnoliaceae; United States; North America; America; Hardwood forest tree; Nyssaceae</EG>
<SD>Modelo previsión; Estimación; Evapotranspiración; Rodal forestal mixto; Xilema; Savia; Cuenca; Hidrología; Comparación interespecífica; Quercus alba; Quercus rubra; Acer rubrum; Liriodendron tulipifera; Tennessee; Composición florística; Recurso agua</SD>
<LO>INIST-17223.354000094581190190</LO>
<ID>01-0203679</ID>
</server>
</inist>
</record>

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Transpiration from a multi-species deciduous forest as estimated by xylem sap flow techniques

Transpiration from a multi-species deciduous forest as estimated by xylem sap flow techniques

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