Dr. Monica G.Turner
Department of Integrative Biology
University of Wisconsin
430 Lincoln Dr.
Madison, WI 53706
Ecosystem and
Landscape Ecology Lab
 

Mitchell, C. E.  2000. Effects of land use and habitat fragmentation on mesic forest myrmecochores and ant communities in the southern Appalachian highlands. MS Thesis, University of Wisconsin, Madison.

Although the consequences of habitat fragmentation have been a rich field of inquiry for some time, the ecological legacies of past land use are only recently gaining much attention.  Our work focused on the effects of patch size and historical land use on woodland ants and myrmecochores (plants species that have their diaspores dispersed by ants) in mesic forests of the southern Appalachian Highlands.  The purpose of this study was to examine a potential mechanism, the presence and diversity of seed-dispersing ants, that might explain the reduced abundance and diversity of myrmecochores in small forest patches with high intensities of past land use (Pearson et al. 1998).

Small patches (<25 ha) of forest that had experienced high past land use intensity harbored a greater abundance and diversity of myrmecochorous ants, but a lower abundance and species richness of myrmecochores than did large patches (>200 ha) with minimal past land use.  Overall, sites with greater myrmecochore species richness and abundance had less diverse ant communities and a lower abundance of ants.  This negative correlation was most pronounced among small patches with high levels of prior land use.  Ant species composition varied most between patches that differed in size.  Large patches were dominated by one ant species, Aphaenogaster fulva, whereas small patches supported less A. fulva, but higher numbers of Aphaenogaster rudis and two Camponotus species.  Large patches with low levels of past land use tended to have relatively lower numbers of conspecific immature myrmecochores when adult myrmecochores were more abundant.  In contrast, higher immature abundance was correlated with greater numbers of adult myrmecochores in both small and large patches with high past land use intensity.

An absence of seed-dispersing ants cannot explain the reduced numbers of myrmecochores in small patches with high past land use because the mechanism of seed dispersal by ants still appears to be available in those patches.  Land use legacies or fragmentation effects may be overriding any advantages offered by the increased diversity and abundance of ants at those sites.  The long recovery time and slow recolonization rates, compounded with the low reproduction and slow growth rates of the herbs, may explain some of the myrmecochore patterns we have observed.  It is possible that the reintroduction of adult myrmecochores might reverse extirpation in locations that currently support low numbers and diversities of these herbs.