Abstract

We examined the effects of repeated growing season prescribed fire on the structure and composition of mixed pine–hardwood forests in the southeastern Piedmont region, Georgia, USA. Plots were burned two to four times over an eight-year period with low intensity surface fires during one of four six-week long periods from early April to mid-September. Density of saplings (0.25–11.6 cm diameter at breast height) was significantly reduced after one or two fires during the first four-year period. Sapling density declined with additional burning over the next four years, but density of mesic hardwoods including sweetgum (Liquidambar styraciflua) and red maple (Acer rubrum) remained relatively high (~865 stems ha−1). Repeated burning had little effect on density or basal area of trees (≥11.7 cm dbh) and changes in overstory structure were limited to small increases in the quadratic mean diameter of all trees and pines. We found little evidence to suggest differential effects on structure or composition due to timing of burn within the growing season. Although repeated growing season burning alters midstory structure and composition, burning alone is unlikely to result in immediate shifts in overstory composition or structure in mixed pine–hardwood forests of the southeastern Piedmont region.

Highlights

  • Prescribed fire is an important tool for management and restoration of forests around the world [1,2,3,4,5,6,7]

  • In most cases, growing season burns are considered more effective at reducing woody vegetation than dormant season burns [11,12,13,14]

  • Our results suggest that repeated burning may have little short-term effect on overstory structure and composition, lack of recruitment into smaller size classes from the decreased sapling pool may result in longer-term changes with continued application of prescribed fire

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Summary

Introduction

Prescribed fire is an important tool for management and restoration of forests around the world [1,2,3,4,5,6,7]. Responses to prescribed fire vary among forested ecosystems depending on productivity, species composition, and topography [9]. The effects of prescribed fire usually include reductions in basal area and density, but can vary among species with different life history traits (i.e., re-sprouters vs obligate seeders), as well as among seasons due to differences in phenology and fire intensity [11]. Less is known about how the effects of prescribed fire differ due to variation in timing of application within the growing season, and there is little consensus among studies from different ecosystems [13,14,15,16,17,18].

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