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. 2015 Nov;115(5):389-95.
doi: 10.1038/hdy.2015.35. Epub 2015 Apr 29.

Short-term genetic consequences of habitat loss and fragmentation for the neotropical palm Oenocarpus bataua

Affiliations

Short-term genetic consequences of habitat loss and fragmentation for the neotropical palm Oenocarpus bataua

L Browne et al. Heredity (Edinb). 2015 Nov.

Abstract

Habitat loss and fragmentation may impact animal-mediated dispersal of seed and pollen, and a key question is how the genetic attributes of plant populations respond to these changes. Theory predicts that genetic diversity may be less sensitive to such disruptions in the short term, whereas inbreeding and genetic structure may respond more strongly. However, results from studies to date vary in relation to species, context and the parameter being assessed, triggering calls for more empirical studies, especially from the tropics, where plant-animal dispersal mutualisms are both disproportionately common and at risk. We compared the genetic characteristics of adults and recruits in a long-lived palm Oenocarpus bataua in a recently fragmented landscape (<2 generations) in northwest Ecuador using a suite of 10 polymorphic microsatellite markers. We sampled individuals from six forest fragments and one nearby continuous forest. Our goal was to assess short-term consequences of fragmentation, with a focus on how well empirical data from this system follow theoretical expectations. Mostly congruent with predictions, we found stronger genetic differentiation and fine-scale spatial genetic structure among recruits in fragments compared with recruits in continuous forest, but we did not record differences in genetic diversity or inbreeding, nor did we record any differences between adults in fragments and adults in continuous forest. Our findings suggest that genetic characteristics of populations vary in their sensitivity to change in response to habitat loss and fragmentation, and that fine-scale spatial genetic structure may be a particularly useful indicator of genetic change in recently fragmented landscapes.

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Figures

Figure 1
Figure 1
Map of study area showing location of (a) Mache-Chindul Reserve shaded gray and Bilsa Biological Station (BBS) shaded black in Esmeraldas and Manabí provinces, Ecuador; (b) BBS shaded gray, 130 ha study plot within BBS shaded black, and the six forest fragments sampled in this study. Area (ha) of each location and distance from BBS are provided in Table 1. Map only shows fragments sampled in this study, not all fragments actually present the study area (see Materials and methods ‘Study species and sites').
Figure 2
Figure 2
Spatial autocorrelation analysis of Oenocarpus bataua for (a) adults, (b) beneath recruits and (c) dispersed recruits in Bilsa Biological Station (BBS, solid gray line with circle) and fragments (dashed black line with triangle). Relationship coefficient (Fij) plotted against distance. Error bars are ±1s.e. estimated by jackknifing across loci. The maximum distance was truncated at 350 m to improve clarity.

References

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