Communities of arbuscular mycorrhizal fungi associated with perennial grasses of different forage quality exposed to defoliation

Vegetation management practices, such as defoliation may alter the composition of plant communities and/or the fungi-forming arbuscular mycorrhiza (AMF). We determined the species identity, density, frequency and diversity of AMF spores from soil under the canopies of three native perennial grass sp...

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Autor principal: Ambrosino, M.L
Otros Autores: Cabello, M.N, Busso, C.A, Velázquez, M.S, Torres, Y.A, Cardillo, D.S, Ithurrart, L.S, Montenegro, O.A, Giorgetti, H., Rodriguez, G.
Formato: Capítulo de libro
Lenguaje:Inglés
Publicado: Academic Press 2018
Acceso en línea:Registro en Scopus
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100 1 |a Ambrosino, M.L. 
245 1 0 |a Communities of arbuscular mycorrhizal fungi associated with perennial grasses of different forage quality exposed to defoliation 
260 |b Academic Press  |c 2018 
270 1 0 |m Busso, C.A.; CERZOS [Centro de Recursos Naturales Renovables de la Zona Semiárida (CONICET)], Departamento de Agronomía-Universidad Nacional del SurArgentina; email: carlosbusso1@gmail.com 
506 |2 openaire  |e Política editorial 
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520 3 |a Vegetation management practices, such as defoliation may alter the composition of plant communities and/or the fungi-forming arbuscular mycorrhiza (AMF). We determined the species identity, density, frequency and diversity of AMF spores from soil under the canopies of three native perennial grass species in rangelands of Argentina: 1) Poa ligularis and Nassella tenuis (preferred by livestock) and 2) Amelichloa ambigua (not preferred). For each species, plants either remained undefoliated or were defoliated twice to a 5 cm stubble height during the growing season. Most active meristems remained on the plants after defoliations. AMF communities were sampled prior to (i.e., 48 soil samples) and following (i.e., 72 soil samples) each defoliation event. Spores were grouped in 15 morphospecies. Density, richness and diversity of AMF spores were not influenced by defoliation, and species richness and diversity of AMF were similar among species. Total spore density was greatest for P. ligularis at the sampling prior to defoliation, but this difference did not persist following the defoliation events. The most abundant AMF families were: Acaulosporaceae, Diversisporaceae and Glomeraceae. These results demonstrate that responses of the studied variables were insensitive to the defoliation treatments, and were largely unaffected by the studied grass species. © 2018  |l eng 
536 |a Detalles de la financiación: CIC, Comisión de Investigaciones Científicas 
536 |a Detalles de la financiación: PGI 24/A196, UNS, Universidad Nacional del Sur 
536 |a Detalles de la financiación: CONICET, Consejo Nacional de Investigaciones Científicas y Técnicas 
536 |a Detalles de la financiación: CIC, Construction Industry Council 
536 |a Detalles de la financiación: PIP 00211, CONICET, Consejo Nacional de Investigaciones Científicas y Técnicas 
536 |a Detalles de la financiación: We thank Universidad Nacional del Sur (UNS, PGI 24/A196 ), the Consejo Nacional de Investigaciones Científicas y Técnicas de la República Argentina (CONICET, PIP 00211 ) and the Comisión de Investigaciones Científicas de la Provincia de Buenos Aires (CIC) for providing financial support to C.A.B and M.N.C. The Chacra Experimental Patagones, Ministerio de Asuntos Agrarios, Province of Buenos Aires provided the facilities where this study was conducted. We appreciate very much the work made by the native English speaker Dr. Justin Derner [Research Leader, USDA-ARS Rangeland Resources and Systems Research Unit Director, Central Plains Experimental Range Long-Term Agroecosystem Research (LTAR) site, Cheyenne, WY] for improving the English language of a late version of this manuscript. 
593 |a CONICET (Consejo Nacional de Investigaciones Científicas y Técnicas de la República Argentina), Facultad de Ciencias Exactas y Naturales, Universidad Nacional de La Pampa, Santa Rosa, Provincia de La Pampa, Argentina 
593 |a CIC (Comisión de Investigaciones Científicas de la Provincia de Buenos Aires), Instituto de Botánica Spegazzini, Facultad de Ciencias Naturales y Museo, Universidad Nacional de la Plata (UNLP), La Plata, Buenos Aires, Argentina 
593 |a CERZOS [Centro de Recursos Naturales Renovables de la Zona Semiárida (CONICET)], Departamento de Agronomía-Universidad Nacional del Sur, Bahía Blanca, Provincia de Buenos Aires, Argentina 
593 |a CONICET, Instituto de Botánica Spegazzini, Facultad de Ciencias Naturales y Museo (UNLP), La Plata, Buenos Aires, Argentina 
593 |a CIC, Departamento de Agronomía -Universidad Nacional del Sur, Bahía Blanca, Provincia de Buenos Aires, Argentina 
593 |a CERZOS - CONICETProvincia de Buenos Aires, Argentina 
593 |a Chacra Experimental de Patagones, Ministerio de Asuntos Agrarios, Carmen de Patagones, Provincia de Buenos Aires, Argentina 
690 1 0 |a AMELICHLOA AMBIGUA 
690 1 0 |a DEFOLIATION 
690 1 0 |a NASSELLA TENUIS 
690 1 0 |a POA LIGULARIS 
690 1 0 |a RANGELANDS 
690 1 0 |a ARBUSCULAR MYCORRHIZA 
690 1 0 |a DEFOLIATION 
690 1 0 |a FOOD QUALITY 
690 1 0 |a FORAGE 
690 1 0 |a FUNGUS 
690 1 0 |a GRASS 
690 1 0 |a GROWING SEASON 
690 1 0 |a MANAGEMENT PRACTICE 
690 1 0 |a PERENNIAL PLANT 
690 1 0 |a PLANT COMMUNITY 
690 1 0 |a RANGELAND 
690 1 0 |a SPECIES DIVERSITY 
690 1 0 |a SPECIES RICHNESS 
690 1 0 |a ACAULOSPORACEAE 
690 1 0 |a DIVERSISPORACEAE 
690 1 0 |a FUNGI 
690 1 0 |a GLOMERACEAE 
690 1 0 |a NASSELLA TENUIS 
690 1 0 |a POA LIGULARIS 
690 1 0 |a POACEAE 
700 1 |a Cabello, M.N. 
700 1 |a Busso, C.A. 
700 1 |a Velázquez, M.S. 
700 1 |a Torres, Y.A. 
700 1 |a Cardillo, D.S. 
700 1 |a Ithurrart, L.S. 
700 1 |a Montenegro, O.A. 
700 1 |a Giorgetti, H. 
700 1 |a Rodriguez, G. 
773 0 |d Academic Press, 2018  |g v. 154  |h pp. 61-69  |x 01401963  |w (AR-BaUEN)CENRE-5427  |t J. Arid Environ. 
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