Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process

Autores
Ferraina, Antonella; Molina, Cecilia Denisse; Mazia, Noemí; Piñeiro, Gervasio; Miranda, Isabel; Chaneton, Enrique José
Año de publicación
2021
Idioma
inglés
Tipo de recurso
artículo
Estado
versión publicada
Descripción
Woody plant invasion in grasslands is a global problem widely reported during the last decade (Browning et al. 2008; Van Auken 2009; Simberloff et al. 2010; Vilà et al. 2011; Archer et al. 2017). This process involves the successful establishment of shrubs and/or trees in grasslands with strong consequences on its structure (e.g. biomass, diversity and composition) (Zalba & Villamil 2002; Archer 2009), inducing change in cover and diversity of grass species (Vilà et al. 2011; Chaneton et al. 2013). Although woody plant invasion in grasslands occurs worldwide, the mechanisms by which woody plants affect grass biomass, composition and diversity remains under discussion (Hejda et al. 2009; Eldridge et al. 2011). Resource competition has been invoked as one of the main mechanisms in altering the structure and functioning of invaded grassland communities (Levine et al. 2003; Strayer et al. 2006; Simberloff 2011; Vilà et al. 2011), and in the case of woody plant invasion, adult trees appear as superior competitors for light than grasses (Wilson, 1998). However, changes in light conditions promoted by trees may have positive, negative or neutral effects depending on grass photosynthetic pathway (C3 or C4), tree characteristics (deciduous or evergreen) and climate conditions (Mazía et al. 2016). In the case of deciduous tree invaders, environmental conditions beneath the tree canopy could favor C3 winter grasses (Clavijo et al. 2005; Ansley et al. 2019). However, during spring and summer tree shading of deciduous species could exclude light demanding C4 grasses (Belsky 1994; Scholes & Archer 1997; Clavijo et al. 2005). This effect could be counterbalanced by a decrease in atmospheric water demand below the tree canopy, that decreases water stress of grasses, favoring their establishment and growth, even in the case of no-shade-tolerant C4 grasses (Rossi & Villagra 2003; Ansley et al. 2019). In addition to changes in light conditions beneath trees, woody canopy may indirectly modify herbaceous communities by changing soil conditions. Woody plants can alter soil conditions by leaving a soil legacy in invaded patches affecting the plant community composition in the future (Gioria & Pyšek 2015; Kostenko & Bezemer 2020). Soil legacies after tree invasions include changes in soil seed bank, litter quality and quantity, soil microbiota, and nutrients and organic matter, among others. The “soil memory” can maintain the legacy of past plant species composition, even after their removal (Elgersma et al. 2011; in ‘t Zandt et al. 2020). When trees invade grasslands, the type of tree (deciduous, evergreen, N- fixers and the magnitude of mycorrhizal association, among others) may influence the soil legacy, mainly through altering nutrient availabilities, as compared with soil grassland patches where trees were historically absent. Until now, there are few manipulative experiments that have evaluated separately the mechanisms by which the grasslands communities are affected by tree invasions, unravelling possible soil legacy effects vs direct resource competition (Levine et al. 2003; Vilà et al. 2011). To disentangle the relative importance of such mechanisms in explaining changes in the composition, biomass and diversity of a grassland community, it would be necessary to make reciprocal transplants of grasslands species between original habitats (woody or grassland patches) characterized by different light conditions and historical soil legacy. Temperate grasslands represent one of the most modified biomes by cattle husbandry, agriculture and the introduction of exotic woody species (White et al. 2000; Baldi & Paruelo 2008). Argentinian Pampas region was historically characterized by the lack of trees, which were introduced during the colonial period as a source of shade, firewood and as ornamental species (Chaneton et al. 2013). Nowadays several tree species are invasive in the region, mainly Morus alba, Melia azedarach, Gleditsia triacanthos, Ligustrum lucidum and Pinus sp. (Zalba & Villamil 2002). In particular, G. triacanthos had been introduced in the mid-nineteenth century and is currently the most aggressive exotic woody plant species in the region (Ghersa et al. 2002; Fernandez et al. 2017). Because of the expansion of trees into grasslands of the region, there is an increasing interest in studying the effects of woody plant invasions on resident communities and their impact over time (Strayer et al. 2006). In particular, during the last decade several authors have warned about the magnitude of the ongoing tree invasion and their potential impacts on the diversity and composition of the Pampas grasslands (Cuevas & Zalba 2010; Simberloff et al. 2010; Chaneton et al. 2013). The objective of this work was to evaluate the relative importance of the changes in light conditions generated by the invader G. triacanthos L. tree (honey locust), and the historical soil legacy of vegetation (grassland or woody patch origins) in modulating aboveground and belowground biomass, species composition and diversity of a secondary successional grassland invaded by G. triacanthos trees. We established a long-term manipulative reciprocal transplant (soil monoliths) coming from two origins: grasslands (G) and invaded woody patches (W) into three different habitats: open grasslands (OG), woody patches (WP), and artificial shaded grasslands (SG). The artificial shaded treatment (see methods for details) was employed to simulate light conditions beneath a tree canopy, to evaluate if the observed effects on the grassland´s community were based only on modifications in the light conditions or in other additional mechanisms. We postulated the following working hypothesis: 1- Light condition of a habitat, independently of the soil monolith origin (grassland or woody), is a main driver of differences in grassland biomass (aboveground and belowground), diversity and plant functional types. We predict that, independently of the origin, soil monoliths placed in open grasslands will have higher biomass and species diversity than soil monoliths placed beneath trees or artificial shade, and that C4 and C3 species will be dominant in OG and WP, respectively. Alternatively: 2- The soil monolith origin acts as a secondary driver of differences in community biomass, diversity and plant functional types due to differences in soil legacy, according to the soil monolith origin (grassland or woody habitat). We predict that woody soil monoliths placed in open grasslands, beneath the tree canopy or under artificial shade, will always have lower biomass, lower species diversity and more dominated by C3 species than soil monoliths coming from grasslands.
Fil: Ferraina, Antonella. Instituto Nacional de Tecnología Agropecuaria (INTA). Instituto de Clima y Agua; Argentina
Fil: Molina, Cecilia Denisse. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
Fil: Mazía, Noemí. Universidad de Buenos Aires. Facultad de Agronomía. Departamento de Producción Vegetal; Argentina
Fil: Piñeiro, Gervasio. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
Fil: Miranda, Isabel. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
Fil: Chaneton, Enrique Jose. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
Fuente
Journal of vegetation science 32 (5) : e13074 (Septembre - october 2021)
Materia
Grasslands
Biomass
Praderas
Biomasa
C3 Grasses
C4 Grasses
Plant Functional Types
Herbaceous Biomass
Light Competition
Hierbas C3
Hierbas C4
Tipos Funcionales de Plantas
Biomasa Herbácea
Competencia Ligera
Nivel de accesibilidad
acceso restringido
Condiciones de uso
http://creativecommons.org/licenses/by-nc-sa/4.0/
Repositorio
INTA Digital (INTA)
Institución
Instituto Nacional de Tecnología Agropecuaria
OAI Identificador
oai:localhost:20.500.12123/14856

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spelling Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the processFerraina, AntonellaMolina, Cecilia DenisseMazia, NoemíPiñeiro, GervasioMiranda, IsabelChaneton, Enrique JoséGrasslandsBiomassPraderasBiomasaC3 GrassesC4 GrassesPlant Functional TypesHerbaceous BiomassLight CompetitionHierbas C3Hierbas C4Tipos Funcionales de PlantasBiomasa HerbáceaCompetencia LigeraWoody plant invasion in grasslands is a global problem widely reported during the last decade (Browning et al. 2008; Van Auken 2009; Simberloff et al. 2010; Vilà et al. 2011; Archer et al. 2017). This process involves the successful establishment of shrubs and/or trees in grasslands with strong consequences on its structure (e.g. biomass, diversity and composition) (Zalba & Villamil 2002; Archer 2009), inducing change in cover and diversity of grass species (Vilà et al. 2011; Chaneton et al. 2013). Although woody plant invasion in grasslands occurs worldwide, the mechanisms by which woody plants affect grass biomass, composition and diversity remains under discussion (Hejda et al. 2009; Eldridge et al. 2011). Resource competition has been invoked as one of the main mechanisms in altering the structure and functioning of invaded grassland communities (Levine et al. 2003; Strayer et al. 2006; Simberloff 2011; Vilà et al. 2011), and in the case of woody plant invasion, adult trees appear as superior competitors for light than grasses (Wilson, 1998). However, changes in light conditions promoted by trees may have positive, negative or neutral effects depending on grass photosynthetic pathway (C3 or C4), tree characteristics (deciduous or evergreen) and climate conditions (Mazía et al. 2016). In the case of deciduous tree invaders, environmental conditions beneath the tree canopy could favor C3 winter grasses (Clavijo et al. 2005; Ansley et al. 2019). However, during spring and summer tree shading of deciduous species could exclude light demanding C4 grasses (Belsky 1994; Scholes & Archer 1997; Clavijo et al. 2005). This effect could be counterbalanced by a decrease in atmospheric water demand below the tree canopy, that decreases water stress of grasses, favoring their establishment and growth, even in the case of no-shade-tolerant C4 grasses (Rossi & Villagra 2003; Ansley et al. 2019). In addition to changes in light conditions beneath trees, woody canopy may indirectly modify herbaceous communities by changing soil conditions. Woody plants can alter soil conditions by leaving a soil legacy in invaded patches affecting the plant community composition in the future (Gioria & Pyšek 2015; Kostenko & Bezemer 2020). Soil legacies after tree invasions include changes in soil seed bank, litter quality and quantity, soil microbiota, and nutrients and organic matter, among others. The “soil memory” can maintain the legacy of past plant species composition, even after their removal (Elgersma et al. 2011; in ‘t Zandt et al. 2020). When trees invade grasslands, the type of tree (deciduous, evergreen, N- fixers and the magnitude of mycorrhizal association, among others) may influence the soil legacy, mainly through altering nutrient availabilities, as compared with soil grassland patches where trees were historically absent. Until now, there are few manipulative experiments that have evaluated separately the mechanisms by which the grasslands communities are affected by tree invasions, unravelling possible soil legacy effects vs direct resource competition (Levine et al. 2003; Vilà et al. 2011). To disentangle the relative importance of such mechanisms in explaining changes in the composition, biomass and diversity of a grassland community, it would be necessary to make reciprocal transplants of grasslands species between original habitats (woody or grassland patches) characterized by different light conditions and historical soil legacy. Temperate grasslands represent one of the most modified biomes by cattle husbandry, agriculture and the introduction of exotic woody species (White et al. 2000; Baldi & Paruelo 2008). Argentinian Pampas region was historically characterized by the lack of trees, which were introduced during the colonial period as a source of shade, firewood and as ornamental species (Chaneton et al. 2013). Nowadays several tree species are invasive in the region, mainly Morus alba, Melia azedarach, Gleditsia triacanthos, Ligustrum lucidum and Pinus sp. (Zalba & Villamil 2002). In particular, G. triacanthos had been introduced in the mid-nineteenth century and is currently the most aggressive exotic woody plant species in the region (Ghersa et al. 2002; Fernandez et al. 2017). Because of the expansion of trees into grasslands of the region, there is an increasing interest in studying the effects of woody plant invasions on resident communities and their impact over time (Strayer et al. 2006). In particular, during the last decade several authors have warned about the magnitude of the ongoing tree invasion and their potential impacts on the diversity and composition of the Pampas grasslands (Cuevas & Zalba 2010; Simberloff et al. 2010; Chaneton et al. 2013). The objective of this work was to evaluate the relative importance of the changes in light conditions generated by the invader G. triacanthos L. tree (honey locust), and the historical soil legacy of vegetation (grassland or woody patch origins) in modulating aboveground and belowground biomass, species composition and diversity of a secondary successional grassland invaded by G. triacanthos trees. We established a long-term manipulative reciprocal transplant (soil monoliths) coming from two origins: grasslands (G) and invaded woody patches (W) into three different habitats: open grasslands (OG), woody patches (WP), and artificial shaded grasslands (SG). The artificial shaded treatment (see methods for details) was employed to simulate light conditions beneath a tree canopy, to evaluate if the observed effects on the grassland´s community were based only on modifications in the light conditions or in other additional mechanisms. We postulated the following working hypothesis: 1- Light condition of a habitat, independently of the soil monolith origin (grassland or woody), is a main driver of differences in grassland biomass (aboveground and belowground), diversity and plant functional types. We predict that, independently of the origin, soil monoliths placed in open grasslands will have higher biomass and species diversity than soil monoliths placed beneath trees or artificial shade, and that C4 and C3 species will be dominant in OG and WP, respectively. Alternatively: 2- The soil monolith origin acts as a secondary driver of differences in community biomass, diversity and plant functional types due to differences in soil legacy, according to the soil monolith origin (grassland or woody habitat). We predict that woody soil monoliths placed in open grasslands, beneath the tree canopy or under artificial shade, will always have lower biomass, lower species diversity and more dominated by C3 species than soil monoliths coming from grasslands.Fil: Ferraina, Antonella. Instituto Nacional de Tecnología Agropecuaria (INTA). Instituto de Clima y Agua; ArgentinaFil: Molina, Cecilia Denisse. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.Fil: Mazía, Noemí. Universidad de Buenos Aires. Facultad de Agronomía. Departamento de Producción Vegetal; ArgentinaFil: Piñeiro, Gervasio. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.Fil: Miranda, Isabel. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.Fil: Chaneton, Enrique Jose. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.Wiley2023-08-02T14:11:11Z2023-08-02T14:11:11Z2021-08-21info:eu-repo/semantics/articleinfo:eu-repo/semantics/publishedVersionhttp://purl.org/coar/resource_type/c_6501info:ar-repo/semantics/articuloapplication/pdfhttp://hdl.handle.net/20.500.12123/14856https://onlinelibrary.wiley.com/doi/10.1111/jvs.130741100-9233https://doi.org/10.1111/jvs.13074Journal of vegetation science 32 (5) : e13074 (Septembre - october 2021)reponame:INTA Digital (INTA)instname:Instituto Nacional de Tecnología Agropecuariaenginfo:eu-repo/semantics/restrictedAccesshttp://creativecommons.org/licenses/by-nc-sa/4.0/Creative Commons Attribution-NonCommercial-ShareAlike 4.0 International (CC BY-NC-SA 4.0)2025-09-29T13:45:57Zoai:localhost:20.500.12123/14856instacron:INTAInstitucionalhttp://repositorio.inta.gob.ar/Organismo científico-tecnológicoNo correspondehttp://repositorio.inta.gob.ar/oai/requesttripaldi.nicolas@inta.gob.arArgentinaNo correspondeNo correspondeNo correspondeopendoar:l2025-09-29 13:45:57.7INTA Digital (INTA) - Instituto Nacional de Tecnología Agropecuariafalse
dc.title.none.fl_str_mv Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
title Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
spellingShingle Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
Ferraina, Antonella
Grasslands
Biomass
Praderas
Biomasa
C3 Grasses
C4 Grasses
Plant Functional Types
Herbaceous Biomass
Light Competition
Hierbas C3
Hierbas C4
Tipos Funcionales de Plantas
Biomasa Herbácea
Competencia Ligera
title_short Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
title_full Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
title_fullStr Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
title_full_unstemmed Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
title_sort Tree invasion in secondary grasslands diminishes herbaceous biomass and diversity: A study of mechanisms behind the process
dc.creator.none.fl_str_mv Ferraina, Antonella
Molina, Cecilia Denisse
Mazia, Noemí
Piñeiro, Gervasio
Miranda, Isabel
Chaneton, Enrique José
author Ferraina, Antonella
author_facet Ferraina, Antonella
Molina, Cecilia Denisse
Mazia, Noemí
Piñeiro, Gervasio
Miranda, Isabel
Chaneton, Enrique José
author_role author
author2 Molina, Cecilia Denisse
Mazia, Noemí
Piñeiro, Gervasio
Miranda, Isabel
Chaneton, Enrique José
author2_role author
author
author
author
author
dc.subject.none.fl_str_mv Grasslands
Biomass
Praderas
Biomasa
C3 Grasses
C4 Grasses
Plant Functional Types
Herbaceous Biomass
Light Competition
Hierbas C3
Hierbas C4
Tipos Funcionales de Plantas
Biomasa Herbácea
Competencia Ligera
topic Grasslands
Biomass
Praderas
Biomasa
C3 Grasses
C4 Grasses
Plant Functional Types
Herbaceous Biomass
Light Competition
Hierbas C3
Hierbas C4
Tipos Funcionales de Plantas
Biomasa Herbácea
Competencia Ligera
dc.description.none.fl_txt_mv Woody plant invasion in grasslands is a global problem widely reported during the last decade (Browning et al. 2008; Van Auken 2009; Simberloff et al. 2010; Vilà et al. 2011; Archer et al. 2017). This process involves the successful establishment of shrubs and/or trees in grasslands with strong consequences on its structure (e.g. biomass, diversity and composition) (Zalba & Villamil 2002; Archer 2009), inducing change in cover and diversity of grass species (Vilà et al. 2011; Chaneton et al. 2013). Although woody plant invasion in grasslands occurs worldwide, the mechanisms by which woody plants affect grass biomass, composition and diversity remains under discussion (Hejda et al. 2009; Eldridge et al. 2011). Resource competition has been invoked as one of the main mechanisms in altering the structure and functioning of invaded grassland communities (Levine et al. 2003; Strayer et al. 2006; Simberloff 2011; Vilà et al. 2011), and in the case of woody plant invasion, adult trees appear as superior competitors for light than grasses (Wilson, 1998). However, changes in light conditions promoted by trees may have positive, negative or neutral effects depending on grass photosynthetic pathway (C3 or C4), tree characteristics (deciduous or evergreen) and climate conditions (Mazía et al. 2016). In the case of deciduous tree invaders, environmental conditions beneath the tree canopy could favor C3 winter grasses (Clavijo et al. 2005; Ansley et al. 2019). However, during spring and summer tree shading of deciduous species could exclude light demanding C4 grasses (Belsky 1994; Scholes & Archer 1997; Clavijo et al. 2005). This effect could be counterbalanced by a decrease in atmospheric water demand below the tree canopy, that decreases water stress of grasses, favoring their establishment and growth, even in the case of no-shade-tolerant C4 grasses (Rossi & Villagra 2003; Ansley et al. 2019). In addition to changes in light conditions beneath trees, woody canopy may indirectly modify herbaceous communities by changing soil conditions. Woody plants can alter soil conditions by leaving a soil legacy in invaded patches affecting the plant community composition in the future (Gioria & Pyšek 2015; Kostenko & Bezemer 2020). Soil legacies after tree invasions include changes in soil seed bank, litter quality and quantity, soil microbiota, and nutrients and organic matter, among others. The “soil memory” can maintain the legacy of past plant species composition, even after their removal (Elgersma et al. 2011; in ‘t Zandt et al. 2020). When trees invade grasslands, the type of tree (deciduous, evergreen, N- fixers and the magnitude of mycorrhizal association, among others) may influence the soil legacy, mainly through altering nutrient availabilities, as compared with soil grassland patches where trees were historically absent. Until now, there are few manipulative experiments that have evaluated separately the mechanisms by which the grasslands communities are affected by tree invasions, unravelling possible soil legacy effects vs direct resource competition (Levine et al. 2003; Vilà et al. 2011). To disentangle the relative importance of such mechanisms in explaining changes in the composition, biomass and diversity of a grassland community, it would be necessary to make reciprocal transplants of grasslands species between original habitats (woody or grassland patches) characterized by different light conditions and historical soil legacy. Temperate grasslands represent one of the most modified biomes by cattle husbandry, agriculture and the introduction of exotic woody species (White et al. 2000; Baldi & Paruelo 2008). Argentinian Pampas region was historically characterized by the lack of trees, which were introduced during the colonial period as a source of shade, firewood and as ornamental species (Chaneton et al. 2013). Nowadays several tree species are invasive in the region, mainly Morus alba, Melia azedarach, Gleditsia triacanthos, Ligustrum lucidum and Pinus sp. (Zalba & Villamil 2002). In particular, G. triacanthos had been introduced in the mid-nineteenth century and is currently the most aggressive exotic woody plant species in the region (Ghersa et al. 2002; Fernandez et al. 2017). Because of the expansion of trees into grasslands of the region, there is an increasing interest in studying the effects of woody plant invasions on resident communities and their impact over time (Strayer et al. 2006). In particular, during the last decade several authors have warned about the magnitude of the ongoing tree invasion and their potential impacts on the diversity and composition of the Pampas grasslands (Cuevas & Zalba 2010; Simberloff et al. 2010; Chaneton et al. 2013). The objective of this work was to evaluate the relative importance of the changes in light conditions generated by the invader G. triacanthos L. tree (honey locust), and the historical soil legacy of vegetation (grassland or woody patch origins) in modulating aboveground and belowground biomass, species composition and diversity of a secondary successional grassland invaded by G. triacanthos trees. We established a long-term manipulative reciprocal transplant (soil monoliths) coming from two origins: grasslands (G) and invaded woody patches (W) into three different habitats: open grasslands (OG), woody patches (WP), and artificial shaded grasslands (SG). The artificial shaded treatment (see methods for details) was employed to simulate light conditions beneath a tree canopy, to evaluate if the observed effects on the grassland´s community were based only on modifications in the light conditions or in other additional mechanisms. We postulated the following working hypothesis: 1- Light condition of a habitat, independently of the soil monolith origin (grassland or woody), is a main driver of differences in grassland biomass (aboveground and belowground), diversity and plant functional types. We predict that, independently of the origin, soil monoliths placed in open grasslands will have higher biomass and species diversity than soil monoliths placed beneath trees or artificial shade, and that C4 and C3 species will be dominant in OG and WP, respectively. Alternatively: 2- The soil monolith origin acts as a secondary driver of differences in community biomass, diversity and plant functional types due to differences in soil legacy, according to the soil monolith origin (grassland or woody habitat). We predict that woody soil monoliths placed in open grasslands, beneath the tree canopy or under artificial shade, will always have lower biomass, lower species diversity and more dominated by C3 species than soil monoliths coming from grasslands.
Fil: Ferraina, Antonella. Instituto Nacional de Tecnología Agropecuaria (INTA). Instituto de Clima y Agua; Argentina
Fil: Molina, Cecilia Denisse. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
Fil: Mazía, Noemí. Universidad de Buenos Aires. Facultad de Agronomía. Departamento de Producción Vegetal; Argentina
Fil: Piñeiro, Gervasio. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
Fil: Miranda, Isabel. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
Fil: Chaneton, Enrique Jose. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina. Universidad de Buenos Aires. Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura; Argentina.
description Woody plant invasion in grasslands is a global problem widely reported during the last decade (Browning et al. 2008; Van Auken 2009; Simberloff et al. 2010; Vilà et al. 2011; Archer et al. 2017). This process involves the successful establishment of shrubs and/or trees in grasslands with strong consequences on its structure (e.g. biomass, diversity and composition) (Zalba & Villamil 2002; Archer 2009), inducing change in cover and diversity of grass species (Vilà et al. 2011; Chaneton et al. 2013). Although woody plant invasion in grasslands occurs worldwide, the mechanisms by which woody plants affect grass biomass, composition and diversity remains under discussion (Hejda et al. 2009; Eldridge et al. 2011). Resource competition has been invoked as one of the main mechanisms in altering the structure and functioning of invaded grassland communities (Levine et al. 2003; Strayer et al. 2006; Simberloff 2011; Vilà et al. 2011), and in the case of woody plant invasion, adult trees appear as superior competitors for light than grasses (Wilson, 1998). However, changes in light conditions promoted by trees may have positive, negative or neutral effects depending on grass photosynthetic pathway (C3 or C4), tree characteristics (deciduous or evergreen) and climate conditions (Mazía et al. 2016). In the case of deciduous tree invaders, environmental conditions beneath the tree canopy could favor C3 winter grasses (Clavijo et al. 2005; Ansley et al. 2019). However, during spring and summer tree shading of deciduous species could exclude light demanding C4 grasses (Belsky 1994; Scholes & Archer 1997; Clavijo et al. 2005). This effect could be counterbalanced by a decrease in atmospheric water demand below the tree canopy, that decreases water stress of grasses, favoring their establishment and growth, even in the case of no-shade-tolerant C4 grasses (Rossi & Villagra 2003; Ansley et al. 2019). In addition to changes in light conditions beneath trees, woody canopy may indirectly modify herbaceous communities by changing soil conditions. Woody plants can alter soil conditions by leaving a soil legacy in invaded patches affecting the plant community composition in the future (Gioria & Pyšek 2015; Kostenko & Bezemer 2020). Soil legacies after tree invasions include changes in soil seed bank, litter quality and quantity, soil microbiota, and nutrients and organic matter, among others. The “soil memory” can maintain the legacy of past plant species composition, even after their removal (Elgersma et al. 2011; in ‘t Zandt et al. 2020). When trees invade grasslands, the type of tree (deciduous, evergreen, N- fixers and the magnitude of mycorrhizal association, among others) may influence the soil legacy, mainly through altering nutrient availabilities, as compared with soil grassland patches where trees were historically absent. Until now, there are few manipulative experiments that have evaluated separately the mechanisms by which the grasslands communities are affected by tree invasions, unravelling possible soil legacy effects vs direct resource competition (Levine et al. 2003; Vilà et al. 2011). To disentangle the relative importance of such mechanisms in explaining changes in the composition, biomass and diversity of a grassland community, it would be necessary to make reciprocal transplants of grasslands species between original habitats (woody or grassland patches) characterized by different light conditions and historical soil legacy. Temperate grasslands represent one of the most modified biomes by cattle husbandry, agriculture and the introduction of exotic woody species (White et al. 2000; Baldi & Paruelo 2008). Argentinian Pampas region was historically characterized by the lack of trees, which were introduced during the colonial period as a source of shade, firewood and as ornamental species (Chaneton et al. 2013). Nowadays several tree species are invasive in the region, mainly Morus alba, Melia azedarach, Gleditsia triacanthos, Ligustrum lucidum and Pinus sp. (Zalba & Villamil 2002). In particular, G. triacanthos had been introduced in the mid-nineteenth century and is currently the most aggressive exotic woody plant species in the region (Ghersa et al. 2002; Fernandez et al. 2017). Because of the expansion of trees into grasslands of the region, there is an increasing interest in studying the effects of woody plant invasions on resident communities and their impact over time (Strayer et al. 2006). In particular, during the last decade several authors have warned about the magnitude of the ongoing tree invasion and their potential impacts on the diversity and composition of the Pampas grasslands (Cuevas & Zalba 2010; Simberloff et al. 2010; Chaneton et al. 2013). The objective of this work was to evaluate the relative importance of the changes in light conditions generated by the invader G. triacanthos L. tree (honey locust), and the historical soil legacy of vegetation (grassland or woody patch origins) in modulating aboveground and belowground biomass, species composition and diversity of a secondary successional grassland invaded by G. triacanthos trees. We established a long-term manipulative reciprocal transplant (soil monoliths) coming from two origins: grasslands (G) and invaded woody patches (W) into three different habitats: open grasslands (OG), woody patches (WP), and artificial shaded grasslands (SG). The artificial shaded treatment (see methods for details) was employed to simulate light conditions beneath a tree canopy, to evaluate if the observed effects on the grassland´s community were based only on modifications in the light conditions or in other additional mechanisms. We postulated the following working hypothesis: 1- Light condition of a habitat, independently of the soil monolith origin (grassland or woody), is a main driver of differences in grassland biomass (aboveground and belowground), diversity and plant functional types. We predict that, independently of the origin, soil monoliths placed in open grasslands will have higher biomass and species diversity than soil monoliths placed beneath trees or artificial shade, and that C4 and C3 species will be dominant in OG and WP, respectively. Alternatively: 2- The soil monolith origin acts as a secondary driver of differences in community biomass, diversity and plant functional types due to differences in soil legacy, according to the soil monolith origin (grassland or woody habitat). We predict that woody soil monoliths placed in open grasslands, beneath the tree canopy or under artificial shade, will always have lower biomass, lower species diversity and more dominated by C3 species than soil monoliths coming from grasslands.
publishDate 2021
dc.date.none.fl_str_mv 2021-08-21
2023-08-02T14:11:11Z
2023-08-02T14:11:11Z
dc.type.none.fl_str_mv info:eu-repo/semantics/article
info:eu-repo/semantics/publishedVersion
http://purl.org/coar/resource_type/c_6501
info:ar-repo/semantics/articulo
format article
status_str publishedVersion
dc.identifier.none.fl_str_mv http://hdl.handle.net/20.500.12123/14856
https://onlinelibrary.wiley.com/doi/10.1111/jvs.13074
1100-9233
https://doi.org/10.1111/jvs.13074
url http://hdl.handle.net/20.500.12123/14856
https://onlinelibrary.wiley.com/doi/10.1111/jvs.13074
https://doi.org/10.1111/jvs.13074
identifier_str_mv 1100-9233
dc.language.none.fl_str_mv eng
language eng
dc.rights.none.fl_str_mv info:eu-repo/semantics/restrictedAccess
http://creativecommons.org/licenses/by-nc-sa/4.0/
Creative Commons Attribution-NonCommercial-ShareAlike 4.0 International (CC BY-NC-SA 4.0)
eu_rights_str_mv restrictedAccess
rights_invalid_str_mv http://creativecommons.org/licenses/by-nc-sa/4.0/
Creative Commons Attribution-NonCommercial-ShareAlike 4.0 International (CC BY-NC-SA 4.0)
dc.format.none.fl_str_mv application/pdf
dc.publisher.none.fl_str_mv Wiley
publisher.none.fl_str_mv Wiley
dc.source.none.fl_str_mv Journal of vegetation science 32 (5) : e13074 (Septembre - october 2021)
reponame:INTA Digital (INTA)
instname:Instituto Nacional de Tecnología Agropecuaria
reponame_str INTA Digital (INTA)
collection INTA Digital (INTA)
instname_str Instituto Nacional de Tecnología Agropecuaria
repository.name.fl_str_mv INTA Digital (INTA) - Instituto Nacional de Tecnología Agropecuaria
repository.mail.fl_str_mv tripaldi.nicolas@inta.gob.ar
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