期刊
APPLIED VEGETATION SCIENCE
卷 23, 期 1, 页码 14-25出版社
WILEY
DOI: 10.1111/avsc.12457
关键词
abandoned pasture; African grasses; cerrado; natural regeneration; old-growth savanna; recovery rate; resilience; savanna restoration; secondary savanna; tropical grassy biomes; tropical savanna
资金
- Fundacao de Amparo a Pesquisa do Estado de Sao Paulo -FAPESP [2015/23131-9, 2016/17888-2, 2013/50421-2]
- Conselho Nacional de Desenvolvimento Cientifico e Tecnologico -CNPq [303402/2012-1, 312045/2013-1, 312292/2016-3]
- Coordenacao de Aperfeicoamento de Pessoal de Nivel Superior -CAPES [88881.068425/2014-01, 3618/2016, 3632/2016]
Question Assessing the natural regeneration potential of degraded savannas is a crucial step in restoration planning, since that assessment will define the need for and costs of active intervention. Predicting natural regeneration, however, depends on the mechanistic understanding of ecosystem resilience. Here, we searched for the factors modulating plant communities spontaneously regenerating in abandoned pastures. Location Tropical savanna (cerrado), Brazil. Methods Over two years, we quantified changes in the structure, richness and species composition of plant communities in 29 secondary savannas resulting from pasture abandonment. We then investigated the influence of soil and landscape attributes, exotic grass cover and time since pasture abandonment on the recovery rate and species composition of these communities. Results The wide variation among sites was not explained by time since abandonment or distance to the nearest remnant native vegetation. Soil attributes, exotic grasses and native vegetation cover around a pasture explained a small fraction of the variation in the recovery rate. We did not find an isolated factor or a robust set of factors explaining the variation in the recovery rate for all vegetation attributes. Species composition was slightly influenced by exotic grasses, soil penetration resistance, proportion of fine soil particles and time since abandonment. Colonization and resprouting by savanna specialists over the two-year period were hindered by exotic grasses. Conclusion The use of predictive models based on soil properties, exotic grasses, landscape attributes or time since abandonment is unfeasible for inferring the recovery rate of savanna structure and richness after pasture abandonment. Case-by-case monitoring is required to support decisions on restoration intervention. Other factors, which are almost impossible to obtain, such as land-use practices and history and the taxonomic or functional composition of pre-existing vegetation, can potentially influence the recovery rate. Exotic grasses must be controlled to favour colonization and resprouting by savanna specialists.
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