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Last Update 02/04/2009

 

 

    
     
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Edge-mediated succession and drought response in a plant community

 

Elise M. Tulloss and Scott J. Meiners

Department of Biological Sciences, Eastern Illinois University

 

Introduction

 

Edges are important in determining community structure but their impact on community dynamics is relatively unknown.  Edges can mediate succession by buffering communities on either side through changes in climatic factors across edges.  We examined patterns of vegetation dynamics along an edge gradient in 1996 and 2001, a time period that included a severe drought in 1999.

 

Objectives

 

Determine possible vegetation patterns across an edge in response to succession and a severe drought.

 

Methods

 

Study Site: Hutcheson Memorial Forest, New Jersey.  A grid was stretched across the forest-field edge and divided into 1m2 plots.  The site consisted of a mid-successional system with a young forest and fourteen-year-old field.

 

Sampling:  Ten transects run across the forest edge with plots placed at ten meter intervals from the edge.  Each transect went thirty meters into the forest and sixty meters into the field (Figure 1).  Percent ground cover of each understory plant species was recorded in each plot.

 

 

  Figure 1. Sample area transects.

 

Analysis:  Measures of community and population level attributes were analyzed with regression and ANOVA to determine possible edge-mediated succession and drought response patterns.

 

Results

 

Cover, diversity, richness and evenness were lowest in the forest, higher at the edge and highest in the field (Figures 2, 3, 4 and 5). The pattern was consistent between years.

 

 

Figures 2, 3, 4 and 5. Cover, diversity, richness and evenness across the sample area, respectively.

 

Grasses (Figure 6) and exotic species (Figure 7) showed an increase in cover in the field between 1996 and 2001.  This indicated an unexpected pattern of successional reversal.  Some of the species that greatly increased in cover in the field included Achillea millefolium, Agrostis hymenalis, Hieracium pratense and Bromus racemosus.

 

Figure 6. Grass cover across the sample area.

 

Figure 7.  Exotic cover change across the sample area.

 

Species turnover (Figure 8) increased from the forest to the field from 1996 to 2001, showing an increasing replacement in the field following the drought.

 

Figure 8.  Species turnover in the sample area.

 

 

Conclusions

 

The pattern of successional reversal in grasses was likely due to effects of the 1999 drought.  Drought would have created many gaps that would have been filled by early successional species such as grasses.  This was especially important in the field where open conditions are more at risk from drought than the forest interior.


The increase in species turnover with distance from the edge reflects increasing replacement by grass species in the field following drought.


Increasing cover of exotic species in the field suggests area returned to an earlier stage of old field succession following the drought.


Results suggest that the observed pattern is more related to the drought than to the process of succession.  Edges serve primarily as buffers from drought stress.  Areas further from the edge experienced greater community change.

 

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