Hostname: page-component-cd9895bd7-dzt6s Total loading time: 0 Render date: 2024-12-28T12:55:00.677Z Has data issue: false hasContentIssue false

Effects of annual fires on the production of fleshy fruits eaten by birds in a Brazilian Amazonian savanna

Published online by Cambridge University Press:  10 July 2009

Tânia M. Sanaiotti
Affiliation:
Departamento de Ecologia, Instituto Nacional de Pesquisas da Amazônia, Caixa 478, 69.011-970, Manaus – AM, Brazil
William E. Magnusson
Affiliation:
Departamento de Ecologia, Instituto Nacional de Pesquisas da Amazônia, Caixa 478, 69.011-970, Manaus – AM, Brazil

Abstract

This study describes changes in the numbers of plant species fruiting during six years in I ha of Amazonian savanna on the right bank of the Tapajós River, Brazil. The work was based on fleshy fruits from tree and shrub-layer species eaten by birds. The area was burned in the first two years, protected during the following two years and burned again in the last two years. The number of tree species fruiting did not differ significantly between years with and without fire. The number of shrub-layer species fruiting was markedly reduced in years with fire, but the responses varied between species. Data on changes in shrub cover after two consecutive years of fire indicate that species also respond differently in terms of biomass lost due to fires. The two most abundant genera of shrubs, Miconia and Myrcia, had their cover reduced by up to 95% and 72% respectively. The area made available by the loss of shrubs was occupied mainly by the grass Paspalum carinatum. The fires and the decrease in the availability of fruits occurred during the season in which most species of birds breed. An interval of less than three years between fires is insufficient for shrub-layer species to recover.

Resumo

Este estudo descreve mudancas no número de espécies de plantas frutificando durante seis anos em um hectare de savana amazônica à margem direita do Rio Tapajós, Brasil. O estudo baseou-se em espécies arbóreas e espécies do estrato arbustivo com frutos carnosos consumidos por aves. A área foi queimada nos dois primeiros anos, protegida de fogo nos dois anos seguintes e queimada nos dois últimos anos. O número de espécies arbóreas frutificando nāo diferiu entre anos com queimada e anos protegidos de fogo. A frutificaçāo das espécies arbustivas e herbáceas sofreu uma diminuiçāo drástica nos anos com queimada. Porém, as respostas variaram entre espécies. Dados sobre mudanças na área de cobertura de moitas após dois anos consecutivos de fogo indicam que as espécies respondem diferentemente em relaçāo a biomassa reduzida pela queimada. Os dois gêneros arbustivos mais abundantes, Miconia e Myrcia, tiveram suas áreas reduzidas em ate 95% e 72% respectivamente. As áreas reduzidas das moitas foram ocupadas principalmente pelo capim Paspalum carinatum. O peníodo das queimadas e a diminuiçāo na disponibilidade de frutos occoreu durante a estaçāo em que a maioria das espécies de aves reproduzem. Pôde-se concluir que um intervalo menor que três anos entre cada queimada nāo e suficiente para as espécies arbustivas se recuperarem.

Type
Research Article
Copyright
Copyright © Cambridge University Press 1995

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

LITERATURE CITED

Antas, P. de T. Z. 1983. Migração de aves na região do cerrado do Brasil Central. Revista do Serviço Público, Brasilia. Ano 40, 111:159161.Google Scholar
Bastos, M. de N. do C. 1984. Levantamento florístico dos campos do Estado do Pará I – Campo de Joanes (Ilha de Marajó). Boletim do Museu Parainse Emílio Goeldi Botânica 1:6786.Google Scholar
Calder, J. A., Wilson, J. B., Mar, A. F. & Ward, G. 1992. Fire succession and reserve management in a New Zealand snow tussock grassland. Biological Conservation 62:3545.CrossRefGoogle Scholar
Cavalcanti, R. B. 1983. Aves do Cerrado. Revista do Serviço Público, Brasília. Ano 40, 111:6367.Google Scholar
Cavalcanti, R. B. 1988. Conservation of birds in the Cerrado of Central Brazil. Pp. 5966 in Ecology and conservation of grassland birds. ICPB (International Council for Bird Preservation) Technical Publication 7.Google Scholar
Colwing, R. M., Lamont, B. B. & Enricht, N. J. 1990. Fire and management of south-western Australian Banksias. Ecological Society of Australia 16:177183.Google Scholar
Coutinho, L. M. 1982. Ecological effects of fire in Brazilian Cerrado. Pp. 273291 in Hundey, B. J. & Walker, B. H. (eds). Ecological studies 42: Ecology of tropical savannas. Springer-Verlag, Berlin.CrossRefGoogle Scholar
Coutinho, L. M. 1990. Fire in the ecology of Brazilian Cerrado. Pp. 82105 in Goldammer, J. G. (ed.). Fire in the tropical biota: ecosystem and global challenges. Springer-Verlag, Heidelberg.CrossRefGoogle Scholar
Dantas, M. & Rodrigues, I. A. 1982. Estudos fitoecológicos do trópico úmido brasileiro: IV Levantamentos botânicos em campos do Rio Branco. Embrapa-Cpatu (Empresa Brasileira de Pesquisa Agropecuária-Centro de Pesquisa Agroflorestal da Amazônia Oriental). Boletim de Pesquisa 40:131.Google Scholar
Egler, W. A. 1960. Contribuições ao conhecimento dos campos da Amazônia. I – Os campos do Ariramba. Boletim do Museu Paraense Emílio Goeldi Botânica 4:136 + 8 fotos.Google Scholar
Fox, M. D. & Fox, B. J. 1986. The effect of fire frequency on the structure and floristic composition of a woodland understorey. Australian Journal of Ecology 11:7785.CrossRefGoogle Scholar
Furley, P. A. & Ratter, J. A. 1988. Soil resources and plant communities of the central Brazilian cerrado and their development. Journal of Biogeography 15:97108.CrossRefGoogle Scholar
Gottsberger, G. & Morawetz, W. 1986. Floristic, structural and phytogeographical analysis of the savannas of Humaitá (Amazonas). Flora 178:4171.CrossRefGoogle Scholar
Huber, O. 1982. Significance of savanna vegetation in the Amazon Territory of Venezuela. Pp. 221224 in Prance, G. T. (ed.). Biological diversification in the tropics. Columbia University Press, NY.Google Scholar
Janssen, A. 1986. Flora und Vegetation der Savannen von Humaitá und lhre Standortbedingungen. Dissertaciones Botanicae, Berlin. BAND 93.Google Scholar
Kellman, M. 1986. Fire sensitivity of Casuarina torulosa in North Queensland, Australia, Biotropica 18:107110.CrossRefGoogle Scholar
Kubitski, K. 1979. Ocorrência de Kielmeyera nos ‘campos de Humaitá’ e a natureza dos ‘campos’ – Flora da Amazônia. Acta Amazônica 9:401404.CrossRefGoogle Scholar
Lima, D. de A. 1958. Viagem aos campos de Monte Alegre. Contribuição para o conhecimento de sua flora. Boletim Técnico do Instituto Agronômico do Norte 36:99147.Google Scholar
Magnusson, W. E. & Sanaiotti, T. M. 1987. Dispersal of Miconia seeds by the rat Bolomys lasiurus. Journal of Tropical Ecology 3:277278.CrossRefGoogle Scholar
Magnusson, W. E. & Silva, E. V. da. 1993. Relative effects of size, season, and species on the diets of some Amazonian savanna lizards. Journal of Herpetology 27:380385.CrossRefGoogle Scholar
Milliken, W. & Ratter, J. A. 1989. First Report of the Vegetation Survey of the Maracá Rainforest Project (INPA/RGS/SEMA). Royal Botanic Garden, Edinburgh.Google Scholar
Miranda, I. S. 1991. Estrutura e fenologia de uma comunidade arbórea da savana amazônica de Alter-do-Chão, Pará. MSc Thesis. INPA/FUA, Manaus.Google Scholar
Miyanishi, K. & Kellmann, M. 1986. The role of fire in recruitment of two neotropical savanna shrubs, Miconia albicans and Clidemia sericea. Biotropica 18:224230.CrossRefGoogle Scholar
Nieuwenhuis, A. 1987. The effect of fire frequency on the sclerophyll vegetation of the West Head, New South Wales. Australian Journal of Ecology 12:373385.CrossRefGoogle Scholar
Pires, J. M. & Prance, G. T. 1985. The vegetation types of the Brazilian Amazon. Pp. 109145 in Prance, G. T. & Lovejoy, T. E. (eds). Key environments: Amazonia, Chap. 7. Pergamon Press, Oxford.Google Scholar
Pivello, V. R. & Coutinho, L. M. 1992. Transfer of macronutrients to the atmosphere during experimental burnings in an open cerrado (Brazilian savanna). Journal of Tropical Ecology 8:487497.CrossRefGoogle Scholar
Ratter, J. A. 1987. Notes on the vegetation of the Parque Nacional do Araguaia (Brazil). Notes from the Royal Botanic Garden, Edinburgh 44:311342.Google Scholar
Ratter, J. A. & Dargie, T. C. D. 1992. An analysis of the floristic composition of 26 cerrado areas in Brazil. Edinburgh Journal of Botany 49:235250.CrossRefGoogle Scholar
Ratter, J. A., Richards, P. W., Argent, G. & Gifford, D. R. 1973. Observations on the vegetation of northeastern Mato Grosso. I. The woody vegetation types of the Xavantina-Cachimbo expedition area. Philosophical Transactions of the Royal Society of London, B. Biological Sciences 266:449492.Google Scholar
Sanaiotti, T. M. 1987. Area de vida de Formicivora rufa em savana amazônica, Alter do Chão – PA. MSc Thesis. INPA/FUA, Manaus.Google Scholar
San José, J. J. & Fariñas, M. R. 1983. Changes in tree density and species composition in a protected Trachypogon savanna, Venezuela. Ecology 64:447453.CrossRefGoogle Scholar
San José, J. J. & Fariñas, M. R. 1991. Temporal changes in the structure of a Trachypogon savanna protected for 25 years. Acta Ecologica 12:237247.Google Scholar
Silberbauer-Gottsberger, I., Morawetz, W. & Gottsberger, G. 1977. Frost damage of cerrado plants in Botucatu, Brazil, as related to the geographical distribution of the species. Biotropica 9:253261.CrossRefGoogle Scholar
Sudam Projeto de Hidrologia e Climatologia da Amazônia. 1984. Atlas Climatológico da Amazônia Brasileira. Publ. 39.Google Scholar
Takeuchi, M. 1960. The structure of the Amazonian vegetation. I. Savanna in northern Amazon. Journal of the Faculty of Science, University of Tokyo III, 7:523533, 33 plates.Google Scholar
Walker, P. J. & Green, D. R. 1976. A note on the effects on wildlife on trees and shrubs in the Cobar District, New South Wales. Journal of Soil Conservation Service, NSW 35:126132.Google Scholar
Zedler, P. H., Gautier, C. R. & McMaster, G. S. 1983. Vegetation change in response to extreme events: the effect of a short interval between fires in California chaparral and coastal scrub. Ecology 64:809818.CrossRefGoogle Scholar