Nc. Johnson et Da. Wedin, SOIL CARBON, NUTRIENTS, AND MYCORRHIZAE DURING CONVERSION OF DRY TROPICAL FOREST TO GRASSLAND, Ecological applications, 7(1), 1997, pp. 171-182
Wildfires and alien grass invasion threaten dry tropical forests throu
ghout Central America. Efforts to preserve and restore these forests w
ill require a better understanding of how conversion to grassland chan
ges key belowground processes and organisms such as soil organic matte
r, nutrient cycling, and mycorrhizae. We studied forest, edge, and gra
ssland soils from five 60-m transects perpendicular to abrupt forest-g
rassland boundaries in Guanacaste Province, Costa Rica. Nutrient conce
ntrations, N mineralization dynamics, and mycorrhizal fungal communiti
es were compared across vegetation type (forest, edge, and grassland).
The dynamics of N mineralization were measured in year-long laborator
y incubations, and the diversity of mycorrhizal fungal communities was
assessed from populations of soil-borne spores. Soil C, N, and K were
lower, while many base cations and micronutrients were higher in gras
sland plots than in forest plots. Although differences in the quantity
of total soil C and N occurred mainly in the forest-to-edge transitio
n, differences in the quality of soil organic matter, as reflected by
soil C:N ratios and mineralization rates, occurred in the edge-to-gras
sland transition. Beta diversity of mycorrhizal spore communities (mea
sured by Sorenson's similarity index) was lower in the grassland plots
than in the forest plots, indicating that grass invasion had caused s
ome convergence. However, total spore density and alpha diversity of m
ycorrhizal spore communities (measured by species richness and Simpson
's diversity index) were not altered by wildfires and grass invasion.
These results suggest that persistence and regeneration of forest plan
t species in the grasslands may not be constrained to a significant de
gree by the lack of mycorrhizal symbionts. These grasslands appear to
be sustainable, alternative stable states for these areas. Positive fe
edbacks between the alien grassland vegetation and both fire and nutri
ent cycling maintain and reinforce this alternative state.