Functional group dominance and identity effects influence the magnitude of grassland invasion
Summary: Variation in functional community composition is expected to influence the extent of exotic species invasions. Yet, whether resident functional groups control invasion through their relative biomass [mass ratio hypothesis] or by traits other than biomass [identity hypothesis] remains poorly...
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| Otros Autores: | , , , , |
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| Formato: | Artículo |
| Lenguaje: | Inglés |
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| Acceso en línea: | http://ri.agro.uba.ar/files/intranet/articulo/2013longo.pdf LINK AL EDITOR |
| Aporte de: | Registro referencial: Solicitar el recurso aquí |
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| 024 | |a 10.1111/1365-2745.12128 | ||
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| 245 | 1 | 0 | |a Functional group dominance and identity effects influence the magnitude of grassland invasion |
| 520 | |a Summary: Variation in functional community composition is expected to influence the extent of exotic species invasions. Yet, whether resident functional groups control invasion through their relative biomass [mass ratio hypothesis] or by traits other than biomass [identity hypothesis] remains poorly understood. We performed a 6-year experiment to determine the effects of removing different functional groups on exotic species biomass in a Flooding Pampa grassland, Argentina. Functional groups were defined by life-form [grasses or forbs], phenology [winter or summer] and origin [native or exotic]. Removal of each functional group was compared against the removal of an equivalent amount of random biomass. Exotic group responses were monitored over 4 years of continuous removals, and after 2 years of recovery without manipulations. Removal of dominant native summer grasses caused the greatest impact on exotic species and overall community composition. Native summer-grass removal significantly increased exotic grass [120 percent] and forb [730 percent] biomass beyond the level [46 percent and 180 percent, respectively] expected from deleting a similar amount of biomass at random. Exotic annual grasses showed only a transient increase, whereas exotic forb invasion persisted even after 2 years without removals. Removing subordinate, native or exotic winter grasses, and rare native forbs significantly promoted exotic forbs, but to the same level [300 percent] as random biomass removals. Total grass removal increased exotic forbs to half the extent expected from adding the effects of single grass group removals. Dispersal limitation and harsh abiotic conditions may constrain exotic forb spread into such heavily grass-depleted patches. Synthesis. The impact of losing a functional group on the magnitude and persistence of invasion reflected its relative contribution to community biomass. Identity attributes other than biomass [e.g. phenological niche] further enhanced the biotic control that dominant native grasses exerted on established exotic species. Our findings highlight the community legacies of past disturbances to dominant functional groups. | ||
| 653 | 0 | |a BIODIVERSITY | |
| 653 | 0 | |a BIOTIC RESISTANCE | |
| 653 | 0 | |a INVASION ECOLOGY | |
| 653 | 0 | |a MASS RATIO HYPOTHESIS | |
| 653 | 0 | |a PHENOLOGICAL NICHES | |
| 653 | 0 | |a RANK ABUNDANCE | |
| 653 | 0 | |a REMOVAL EXPERIMENT | |
| 653 | 0 | |a SUBADDITIVE EFFECT | |
| 653 | 0 | |a BIOLOGICAL INVASION | |
| 653 | 0 | |a BIOMASS | |
| 653 | 0 | |a COMMUNITY COMPOSITION | |
| 653 | 0 | |a DISPERSAL | |
| 653 | 0 | |a DISTURBANCE | |
| 653 | 0 | |a DOMINANCE | |
| 653 | 0 | |a FUNCTIONAL GROUP | |
| 653 | 0 | |a GRASSLAND | |
| 653 | 0 | |a GROWTH FORM | |
| 653 | 0 | |a INVASIVE SPECIES | |
| 653 | 0 | |a PHENOLOGY | |
| 653 | 0 | |a ARGENTINA | |
| 653 | 0 | |a PAMPAS | |
| 653 | 0 | |a DIGITARIA CILIARIS | |
| 653 | 0 | |a POACEAE | |
| 700 | 1 | |a Longo, María Grisel |9 35860 | |
| 700 | 1 | |a Seidler, Tristram G. |9 72538 | |
| 700 | 1 | |9 31177 |a Garibaldi, Lucas Alejandro | |
| 700 | 1 | |9 12692 |a Tognetti, Pedro Maximiliano | |
| 700 | 1 | |9 6467 |a Chaneton, Enrique José | |
| 773 | |t Journal of Ecology |g vol.101, no.5 (2013), p.1114-1124 | ||
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| 900 | |a ^tFunctional group dominance and identity effects influence the magnitude of grassland invasion | ||
| 900 | |a ^aLongo^bG. | ||
| 900 | |a ^aSeidler^bT.G. | ||
| 900 | |a ^aGaribaldi^bL.A. | ||
| 900 | |a ^aTognetti^bP.M. | ||
| 900 | |a ^aChaneton^bE.J. | ||
| 900 | |a ^aLongo^bG. | ||
| 900 | |a ^aSeidler^bT. G. | ||
| 900 | |a ^aGaribaldi^bL. A. | ||
| 900 | |a ^aTognetti^bP. M. | ||
| 900 | |a ^aChaneton^bE. J. | ||
| 900 | |a ^aLongo^bG.^tIFEVA-CONICET and Facultad de Agronomía, Universidad de Buenos Aires, Av. San Martín 4453, Buenos Aires, 1417, Argentina | ||
| 900 | |a ^aSeidler^bT.G.^tHarvard Forest, 324 N. Main St., Petersham, MA, 01366, United States | ||
| 900 | |a ^aGaribaldi^bL.A.^tSede Andina, Universidad Nacional de Río Negro and CONICET, Mitre 630, San Carlos de Bariloche, 8400, Argentina | ||
| 900 | |a ^aTognetti^bP.M.^tIFEVA-CONICET and Facultad de Agronomía, Universidad de Buenos Aires, Av. San Martín 4453,Buenos Aires, 1417, Argentina | ||
| 900 | |a ^aTognetti^bP.M.^tDepartamento de Métodos Cuantitativos y Sistemas de Información, Facultad de Agronomía, Universidad de Buenos Aires, Av. San Martín 4453, Buenos Aires, 1417, Argentina | ||
| 900 | |a ^aChaneton^bE.J.^tIFEVA-CONICET and Facultad de Agronomía, Universidad de Buenos Aires, Av. San Martín 4453, Buenos Aires,1417, Argentina | ||
| 900 | |a ^tJournal of Ecology^cJ. Ecol. | ||
| 900 | |a en | ||
| 900 | |a 1114 | ||
| 900 | |a ^i | ||
| 900 | |a Vol. 101, no. 5 | ||
| 900 | |a 1124 | ||
| 900 | |a BIODIVERSITY | ||
| 900 | |a BIOTIC RESISTANCE | ||
| 900 | |a INVASION ECOLOGY | ||
| 900 | |a MASS RATIO HYPOTHESIS | ||
| 900 | |a PHENOLOGICAL NICHES | ||
| 900 | |a RANK ABUNDANCE | ||
| 900 | |a REMOVAL EXPERIMENT | ||
| 900 | |a SUBADDITIVE EFFECT | ||
| 900 | |a BIOLOGICAL INVASION | ||
| 900 | |a BIOMASS | ||
| 900 | |a COMMUNITY COMPOSITION | ||
| 900 | |a DISPERSAL | ||
| 900 | |a DISTURBANCE | ||
| 900 | |a DOMINANCE | ||
| 900 | |a FUNCTIONAL GROUP | ||
| 900 | |a GRASSLAND | ||
| 900 | |a GROWTH FORM | ||
| 900 | |a INVASIVE SPECIES | ||
| 900 | |a PHENOLOGY | ||
| 900 | |a ARGENTINA | ||
| 900 | |a PAMPAS | ||
| 900 | |a DIGITARIA CILIARIS | ||
| 900 | |a POACEAE | ||
| 900 | |a Summary: Variation in functional community composition is expected to influence the extent of exotic species invasions. Yet, whether resident functional groups control invasion through their relative biomass [mass ratio hypothesis] or by traits other than biomass [identity hypothesis] remains poorly understood. We performed a 6-year experiment to determine the effects of removing different functional groups on exotic species biomass in a Flooding Pampa grassland, Argentina. Functional groups were defined by life-form [grasses or forbs], phenology [winter or summer] and origin [native or exotic]. Removal of each functional group was compared against the removal of an equivalent amount of random biomass. Exotic group responses were monitored over 4 years of continuous removals, and after 2 years of recovery without manipulations. Removal of dominant native summer grasses caused the greatest impact on exotic species and overall community composition. Native summer-grass removal significantly increased exotic grass [120 percent] and forb [730 percent] biomass beyond the level [46 percent and 180 percent, respectively] expected from deleting a similar amount of biomass at random. Exotic annual grasses showed only a transient increase, whereas exotic forb invasion persisted even after 2 years without removals. Removing subordinate, native or exotic winter grasses, and rare native forbs significantly promoted exotic forbs, but to the same level [300 percent] as random biomass removals. Total grass removal increased exotic forbs to half the extent expected from adding the effects of single grass group removals. Dispersal limitation and harsh abiotic conditions may constrain exotic forb spread into such heavily grass-depleted patches. Synthesis. The impact of losing a functional group on the magnitude and persistence of invasion reflected its relative contribution to community biomass. Identity attributes other than biomass [e.g. phenological niche] further enhanced the biotic control that dominant native grasses exerted on established exotic species. Our findings highlight the community legacies of past disturbances to dominant functional groups. | ||
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