CheneBelgiqueV1, PascalFrancis, Corpus, bibRecord, 000039

Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success

Identifieur interne : 000039 ( PascalFrancis/Corpus ); précédent : 000038; suivant : 000040

Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success

Auteurs : Margot Vanhellemont ; Lander Baeten ; Hans Verbeeck ; Martin Hermy ; Kris Verheyen

Source :

Acta oecologica : (Montrouge) [ 1146-609X ] ; 2011.

RBID : Pascal:11-0229067

Descripteurs français

Pascal (Inist)
- Long terme, Forêt résineuse, Régénération forestière, Houppier, Allométrie, Prunus serotina, Pinus sylvestris, Invasion biologique, Succès.

English descriptors

KwdEn :
- Allometry, Biological invasion, Coniferous forest, Forest regeneration, Long term, Pinus sylvestris, Prunus serotina, Success, Tree crown.

Abstract

The spread of invasive tree species in forests can be slow because of their long life span and the lag phases that may occur during the invasion process. Models of forest succession are a useful tool to explore how these invasive species might affect long-term forest development. We used the spatially explicit individual tree model SORTIE-ND to gain insight into the long-term development of a gap-dependent invasive tree species, Prunus serotina, in a pine-oak forest on sandy soil, the forest type in which P. serotina occurs most often in its introduced range. Forest inventory data, tree ring data, and photographs of the tree crowns were collected in a forest reserve in the Netherlands, characterized by high game densities. The collected data were then combined with data from literature to parameterize the model. We ran the model for two different scenarios in order to evaluate the impact of differences in the regeneration success of the native Quercus robur and the invasive P. serotina. The outcome of the simulations shows two differing courses of forest development. The invasive P. serotina became the dominant species when the regeneration of Q. robur was hindered, e.g., because of high herbivore densities. When both Q. robur and P. serotina were able to regenerate, Q. robur became the most abundant species in the long-term. We hypothesize that the relatively short life span of P. serotina may preclude its dominance if other long-lived tree species are present and able to regenerate.

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

A01	`01`	`1`		`@0 1146-609X`
A03		`1`		`@0 Acta oecol. : (Montrouge)`
A05				`@2 37`
A06				`@2 3`
A08	`01`	`1`	`ENG`	`@1 Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success`
A11	`01`	`1`		`@1 VANHELLEMONT (Margot)`
A11	`02`	`1`		`@1 BAETEN (Lander)`
A11	`03`	`1`		`@1 VERBEECK (Hans)`
A11	`04`	`1`		`@1 HERMY (Martin)`
A11	`05`	`1`		`@1 VERHEYEN (Kris)`
A14	`01`			`@1 Laboratory of Forestry, Ghent University, Geraardsbergsesteenweg 267 @2 9090 Gontrode @3 BEL @Z 1 aut. @Z 2 aut. @Z 5 aut.`
A14	`02`			`@1 Laboratory of Plant Ecology, Ghent University, Coupure Links 653 @2 9000 Ghent @3 BEL @Z 3 aut.`
A14	`03`			`@1 Division Forest, Nature and Landscape, K.U.Leuven, Celestijnenlaan 200e @2 3001 Leuven @3 BEL @Z 4 aut.`
A20				`@1 203-211`
A21				`@1 2011`
A23	`01`			`@0 ENG`
A43	`01`			`@1 INIST @2 12904 @5 354000191477850060`
A44				`@0 0000 @1 © 2011 INIST-CNRS. All rights reserved.`
A45				`@0 1 p.1/4`
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C01	`01`		`ENG`	@0 The spread of invasive tree species in forests can be slow because of their long life span and the lag phases that may occur during the invasion process. Models of forest succession are a useful tool to explore how these invasive species might affect long-term forest development. We used the spatially explicit individual tree model SORTIE-ND to gain insight into the long-term development of a gap-dependent invasive tree species, Prunus serotina, in a pine-oak forest on sandy soil, the forest type in which P. serotina occurs most often in its introduced range. Forest inventory data, tree ring data, and photographs of the tree crowns were collected in a forest reserve in the Netherlands, characterized by high game densities. The collected data were then combined with data from literature to parameterize the model. We ran the model for two different scenarios in order to evaluate the impact of differences in the regeneration success of the native Quercus robur and the invasive P. serotina. The outcome of the simulations shows two differing courses of forest development. The invasive P. serotina became the dominant species when the regeneration of Q. robur was hindered, e.g., because of high herbivore densities. When both Q. robur and P. serotina were able to regenerate, Q. robur became the most abundant species in the long-term. We hypothesize that the relatively short life span of P. serotina may preclude its dominance if other long-lived tree species are present and able to regenerate.
C02	`01`	`X`		`@0 002A14B01`
C02	`02`	`X`		`@0 002A33A02`
C03	`01`	`X`	`FRE`	`@0 Long terme @5 01`
C03	`01`	`X`	`ENG`	`@0 Long term @5 01`
C03	`01`	`X`	`SPA`	`@0 Largo plazo @5 01`
C03	`02`	`X`	`FRE`	`@0 Forêt résineuse @5 02`
C03	`02`	`X`	`ENG`	`@0 Coniferous forest @5 02`
C03	`02`	`X`	`SPA`	`@0 Bosque resinoso @5 02`
C03	`03`	`X`	`FRE`	`@0 Régénération forestière @5 03`
C03	`03`	`X`	`ENG`	`@0 Forest regeneration @5 03`
C03	`03`	`X`	`SPA`	`@0 Regeneración forestal @5 03`
C03	`04`	`X`	`FRE`	`@0 Houppier @5 04`
C03	`04`	`X`	`ENG`	`@0 Tree crown @5 04`
C03	`04`	`X`	`SPA`	`@0 Copa @5 04`
C03	`05`	`X`	`FRE`	`@0 Allométrie @5 05`
C03	`05`	`X`	`ENG`	`@0 Allometry @5 05`
C03	`05`	`X`	`SPA`	`@0 Alometría @5 05`
C03	`06`	`X`	`FRE`	`@0 Prunus serotina @2 NS @5 49`
C03	`06`	`X`	`ENG`	`@0 Prunus serotina @2 NS @5 49`
C03	`06`	`X`	`SPA`	`@0 Prunus serotina @2 NS @5 49`
C03	`07`	`X`	`FRE`	`@0 Pinus sylvestris @2 NS @5 50`
C03	`07`	`X`	`ENG`	`@0 Pinus sylvestris @2 NS @5 50`
C03	`07`	`X`	`SPA`	`@0 Pinus sylvestris @2 NS @5 50`
C03	`08`	`X`	`FRE`	`@0 Invasion biologique @4 CD @5 96`
C03	`08`	`X`	`ENG`	`@0 Biological invasion @4 CD @5 96`
C03	`09`	`X`	`FRE`	`@0 Succès @4 CD @5 97`
C03	`09`	`X`	`ENG`	`@0 Success @4 CD @5 97`
C03	`09`	`X`	`SPA`	`@0 Exito @4 CD @5 97`
C07	`01`	`X`	`FRE`	`@0 Arbre forestier feuillu @5 32`
C07	`01`	`X`	`ENG`	`@0 Hardwood forest tree @5 32`
C07	`01`	`X`	`SPA`	`@0 Arbol forestal frondoso @5 32`
C07	`02`	`X`	`FRE`	`@0 Arbre forestier résineux @5 33`
C07	`02`	`X`	`ENG`	`@0 Softwood forest tree @5 33`
C07	`02`	`X`	`SPA`	`@0 Arbol forestal resinoso @5 33`
C07	`03`	`X`	`FRE`	`@0 Rosaceae @2 NS`
C07	`03`	`X`	`ENG`	`@0 Rosaceae @2 NS`
C07	`03`	`X`	`SPA`	`@0 Rosaceae @2 NS`
C07	`04`	`X`	`FRE`	`@0 Dicotyledones @2 NS`
C07	`04`	`X`	`ENG`	`@0 Dicotyledones @2 NS`
C07	`04`	`X`	`SPA`	`@0 Dicotyledones @2 NS`
C07	`05`	`X`	`FRE`	`@0 Angiospermae @2 NS`
C07	`05`	`X`	`ENG`	`@0 Angiospermae @2 NS`
C07	`05`	`X`	`SPA`	`@0 Angiospermae @2 NS`
C07	`06`	`X`	`FRE`	`@0 Spermatophyta @2 NS`
C07	`06`	`X`	`ENG`	`@0 Spermatophyta @2 NS`
C07	`06`	`X`	`SPA`	`@0 Spermatophyta @2 NS`
C07	`07`	`X`	`FRE`	`@0 Coniferales @2 NS`
C07	`07`	`X`	`ENG`	`@0 Coniferales @2 NS`
C07	`07`	`X`	`SPA`	`@0 Coniferales @2 NS`
C07	`08`	`X`	`FRE`	`@0 Gymnospermae @2 NS`
C07	`08`	`X`	`ENG`	`@0 Gymnospermae @2 NS`
C07	`08`	`X`	`SPA`	`@0 Gymnospermae @2 NS`
N21				`@1 150`
N44	`01`			`@1 OTO`
N82				`@1 OTO`

Format Inist (serveur)

NO :	PASCAL 11-0229067 INIST
ET :	Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success
AU :	VANHELLEMONT (Margot); BAETEN (Lander); VERBEECK (Hans); HERMY (Martin); VERHEYEN (Kris)
AF :	Laboratory of Forestry, Ghent University, Geraardsbergsesteenweg 267/9090 Gontrode/Belgique (1 aut., 2 aut., 5 aut.); Laboratory of Plant Ecology, Ghent University, Coupure Links 653/9000 Ghent/Belgique (3 aut.); Division Forest, Nature and Landscape, K.U.Leuven, Celestijnenlaan 200e/3001 Leuven/Belgique (4 aut.)
DT :	Publication en série; Niveau analytique
SO :	Acta oecologica : (Montrouge); ISSN 1146-609X; Pays-Bas; Da. 2011; Vol. 37; No. 3; Pp. 203-211; Bibl. 1 p.1/4
LA :	Anglais
EA :	The spread of invasive tree species in forests can be slow because of their long life span and the lag phases that may occur during the invasion process. Models of forest succession are a useful tool to explore how these invasive species might affect long-term forest development. We used the spatially explicit individual tree model SORTIE-ND to gain insight into the long-term development of a gap-dependent invasive tree species, Prunus serotina, in a pine-oak forest on sandy soil, the forest type in which P. serotina occurs most often in its introduced range. Forest inventory data, tree ring data, and photographs of the tree crowns were collected in a forest reserve in the Netherlands, characterized by high game densities. The collected data were then combined with data from literature to parameterize the model. We ran the model for two different scenarios in order to evaluate the impact of differences in the regeneration success of the native Quercus robur and the invasive P. serotina. The outcome of the simulations shows two differing courses of forest development. The invasive P. serotina became the dominant species when the regeneration of Q. robur was hindered, e.g., because of high herbivore densities. When both Q. robur and P. serotina were able to regenerate, Q. robur became the most abundant species in the long-term. We hypothesize that the relatively short life span of P. serotina may preclude its dominance if other long-lived tree species are present and able to regenerate.
CC :	002A14B01; 002A33A02
FD :	Long terme; Forêt résineuse; Régénération forestière; Houppier; Allométrie; Prunus serotina; Pinus sylvestris; Invasion biologique; Succès
FG :	Arbre forestier feuillu; Arbre forestier résineux; Rosaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae
ED :	Long term; Coniferous forest; Forest regeneration; Tree crown; Allometry; Prunus serotina; Pinus sylvestris; Biological invasion; Success
EG :	Hardwood forest tree; Softwood forest tree; Rosaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae
SD :	Largo plazo; Bosque resinoso; Regeneración forestal; Copa; Alometría; Prunus serotina; Pinus sylvestris; Exito
LO :	INIST-12904.354000191477850060
ID :	11-0229067

Links to Exploration step

Pascal:11-0229067

Le document en format XML

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<sourceDesc><biblStruct><analytic><title xml:lang="en" level="a">Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success</title>
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<front><div type="abstract" xml:lang="en">The spread of invasive tree species in forests can be slow because of their long life span and the lag phases that may occur during the invasion process. Models of forest succession are a useful tool to explore how these invasive species might affect long-term forest development. We used the spatially explicit individual tree model SORTIE-ND to gain insight into the long-term development of a gap-dependent invasive tree species, Prunus serotina, in a pine-oak forest on sandy soil, the forest type in which P. serotina occurs most often in its introduced range. Forest inventory data, tree ring data, and photographs of the tree crowns were collected in a forest reserve in the Netherlands, characterized by high game densities. The collected data were then combined with data from literature to parameterize the model. We ran the model for two different scenarios in order to evaluate the impact of differences in the regeneration success of the native Quercus robur and the invasive P. serotina. The outcome of the simulations shows two differing courses of forest development. The invasive P. serotina became the dominant species when the regeneration of Q. robur was hindered, e.g., because of high herbivore densities. When both Q. robur and P. serotina were able to regenerate, Q. robur became the most abundant species in the long-term. We hypothesize that the relatively short life span of P. serotina may preclude its dominance if other long-lived tree species are present and able to regenerate.</div>
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<fC01 i1="01" l="ENG"><s0>The spread of invasive tree species in forests can be slow because of their long life span and the lag phases that may occur during the invasion process. Models of forest succession are a useful tool to explore how these invasive species might affect long-term forest development. We used the spatially explicit individual tree model SORTIE-ND to gain insight into the long-term development of a gap-dependent invasive tree species, Prunus serotina, in a pine-oak forest on sandy soil, the forest type in which P. serotina occurs most often in its introduced range. Forest inventory data, tree ring data, and photographs of the tree crowns were collected in a forest reserve in the Netherlands, characterized by high game densities. The collected data were then combined with data from literature to parameterize the model. We ran the model for two different scenarios in order to evaluate the impact of differences in the regeneration success of the native Quercus robur and the invasive P. serotina. The outcome of the simulations shows two differing courses of forest development. The invasive P. serotina became the dominant species when the regeneration of Q. robur was hindered, e.g., because of high herbivore densities. When both Q. robur and P. serotina were able to regenerate, Q. robur became the most abundant species in the long-term. We hypothesize that the relatively short life span of P. serotina may preclude its dominance if other long-lived tree species are present and able to regenerate.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>002A14B01</s0>
</fC02>
<fC02 i1="02" i2="X"><s0>002A33A02</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Long terme</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Long term</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Largo plazo</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Forêt résineuse</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Coniferous forest</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Bosque resinoso</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Régénération forestière</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Forest regeneration</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Regeneración forestal</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Houppier</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Tree crown</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Copa</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Allométrie</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Allometry</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Alometría</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Prunus serotina</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Prunus serotina</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Prunus serotina</s0>
<s2>NS</s2>
<s5>49</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Pinus sylvestris</s0>
<s2>NS</s2>
<s5>50</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Pinus sylvestris</s0>
<s2>NS</s2>
<s5>50</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Pinus sylvestris</s0>
<s2>NS</s2>
<s5>50</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Invasion biologique</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Biological invasion</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Succès</s0>
<s4>CD</s4>
<s5>97</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Success</s0>
<s4>CD</s4>
<s5>97</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Exito</s0>
<s4>CD</s4>
<s5>97</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE"><s0>Arbre forestier feuillu</s0>
<s5>32</s5>
</fC07>
<fC07 i1="01" i2="X" l="ENG"><s0>Hardwood forest tree</s0>
<s5>32</s5>
</fC07>
<fC07 i1="01" i2="X" l="SPA"><s0>Arbol forestal frondoso</s0>
<s5>32</s5>
</fC07>
<fC07 i1="02" i2="X" l="FRE"><s0>Arbre forestier résineux</s0>
<s5>33</s5>
</fC07>
<fC07 i1="02" i2="X" l="ENG"><s0>Softwood forest tree</s0>
<s5>33</s5>
</fC07>
<fC07 i1="02" i2="X" l="SPA"><s0>Arbol forestal resinoso</s0>
<s5>33</s5>
</fC07>
<fC07 i1="03" i2="X" l="FRE"><s0>Rosaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="ENG"><s0>Rosaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="03" i2="X" l="SPA"><s0>Rosaceae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="FRE"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="ENG"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="04" i2="X" l="SPA"><s0>Dicotyledones</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="FRE"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="ENG"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="05" i2="X" l="SPA"><s0>Angiospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="FRE"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="ENG"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="06" i2="X" l="SPA"><s0>Spermatophyta</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="FRE"><s0>Coniferales</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="ENG"><s0>Coniferales</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="07" i2="X" l="SPA"><s0>Coniferales</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="FRE"><s0>Gymnospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="ENG"><s0>Gymnospermae</s0>
<s2>NS</s2>
</fC07>
<fC07 i1="08" i2="X" l="SPA"><s0>Gymnospermae</s0>
<s2>NS</s2>
</fC07>
<fN21><s1>150</s1>
</fN21>
<fN44 i1="01"><s1>OTO</s1>
</fN44>
<fN82><s1>OTO</s1>
</fN82>
</pA>
</standard>
<server><NO>PASCAL 11-0229067 INIST</NO>
<ET>Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success</ET>
<AU>VANHELLEMONT (Margot); BAETEN (Lander); VERBEECK (Hans); HERMY (Martin); VERHEYEN (Kris)</AU>
<AF>Laboratory of Forestry, Ghent University, Geraardsbergsesteenweg 267/9090 Gontrode/Belgique (1 aut., 2 aut., 5 aut.); Laboratory of Plant Ecology, Ghent University, Coupure Links 653/9000 Ghent/Belgique (3 aut.); Division Forest, Nature and Landscape, K.U.Leuven, Celestijnenlaan 200e/3001 Leuven/Belgique (4 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Acta oecologica : (Montrouge); ISSN 1146-609X; Pays-Bas; Da. 2011; Vol. 37; No. 3; Pp. 203-211; Bibl. 1 p.1/4</SO>
<LA>Anglais</LA>
<EA>The spread of invasive tree species in forests can be slow because of their long life span and the lag phases that may occur during the invasion process. Models of forest succession are a useful tool to explore how these invasive species might affect long-term forest development. We used the spatially explicit individual tree model SORTIE-ND to gain insight into the long-term development of a gap-dependent invasive tree species, Prunus serotina, in a pine-oak forest on sandy soil, the forest type in which P. serotina occurs most often in its introduced range. Forest inventory data, tree ring data, and photographs of the tree crowns were collected in a forest reserve in the Netherlands, characterized by high game densities. The collected data were then combined with data from literature to parameterize the model. We ran the model for two different scenarios in order to evaluate the impact of differences in the regeneration success of the native Quercus robur and the invasive P. serotina. The outcome of the simulations shows two differing courses of forest development. The invasive P. serotina became the dominant species when the regeneration of Q. robur was hindered, e.g., because of high herbivore densities. When both Q. robur and P. serotina were able to regenerate, Q. robur became the most abundant species in the long-term. We hypothesize that the relatively short life span of P. serotina may preclude its dominance if other long-lived tree species are present and able to regenerate.</EA>
<CC>002A14B01; 002A33A02</CC>
<FD>Long terme; Forêt résineuse; Régénération forestière; Houppier; Allométrie; Prunus serotina; Pinus sylvestris; Invasion biologique; Succès</FD>
<FG>Arbre forestier feuillu; Arbre forestier résineux; Rosaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae</FG>
<ED>Long term; Coniferous forest; Forest regeneration; Tree crown; Allometry; Prunus serotina; Pinus sylvestris; Biological invasion; Success</ED>
<EG>Hardwood forest tree; Softwood forest tree; Rosaceae; Dicotyledones; Angiospermae; Spermatophyta; Coniferales; Gymnospermae</EG>
<SD>Largo plazo; Bosque resinoso; Regeneración forestal; Copa; Alometría; Prunus serotina; Pinus sylvestris; Exito</SD>
<LO>INIST-12904.354000191477850060</LO>
<ID>11-0229067</ID>
</server>
</inist>
</record>

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Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success

Long-term scenarios of the invasive black cherry in pine-oak forest: Impact of regeneration success

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