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Elliott, Katherine J.; Hendrick, Ronald L.; Major, Amy E.; Vose, James M.; Swank, Wayne T. 1999. Vegetation dynamics after a prescribed fire in the southern Appalachians. Forest Ecology and Management. 114(2-3): 199-213 [1].
SPECIES INCLUDED IN THE SUMMARY:
Common names are used throughout this summary. For a complete list of the common and scientific names
of species discussed in this summary, see the Appendix.
Historic fire regime characteristics for Appalachian oak-hickory-pine and eastern dry oak communities are summarized below:
Fire regime information on the vegetation community studied in this Research Project Summary. Fire regime characteristics are taken from the LANDFIRE Rapid Assessment Vegetation Model [3]. This vegetation model was developed by local experts using available literature and expert opinion as documented in the .pdf files linked from the Potential Natural Vegetation Groups listed below. | |||||
Vegetation Community (Potential Natural Vegetation Group) | Fire severity* | Fire regime characteristics | |||
Percent of fires | Mean interval (years) |
Minimum interval (years) |
Maximum interval (years) |
||
Appalachian oak-hickory-pine | Replacement | 3% | 180 | 30 | 500 |
Mixed | 8% | 65 | 15 | 150 | |
Surface or low | 89% | 6 | 3 | 10 | |
Oak (eastern dry-xeric) | Replacement | 6% | 128 | 50 | 100 |
Mixed | 16% | 50 | 20 | 30 | |
Surface or low | 78% | 10 | 1 | 10 | |
*Fire Severities: Replacement=Any fire that causes greater than 75% top removal of a vegetation-fuel type, resulting in general replacement of existing vegetation; may or may not cause a lethal effect on the plants. Surface or low=Any fire that causes less than 25% upper layer replacement and/or removal in a vegetation-fuel class but burns 5% or more of the area. Mixed=Any fire burning more than 5% of an area that does not qualify as a replacement, surface, or low-severity fire; includes mosaic and other fires that are intermediate in effects [2,3]. |
Strip head fires were used to burn the approximately 300-ha study area. On the ridge, the fire was stand replacing, and the understory was consumed [1,5]. At the low-slope position, the fire was patchy and burned only the understory. Aboveground flame temperatures and heat penetration were measured using heat-sensitive painted tiles. Flame temperatures were measured 1 and 2 m above ground. Belowground heat penetration was measured at the forest floor and in the mineral soil. Temperatures produced and heat penetration depths are summarized below [5].
Above- and belowground temperatures produced by the fire at low, mid-, and ridge positions | ||||
Slope position | Flame temperature (°C) | Average (range) of soil heat penetration (mm) | ||
1 m | 2 m | 45 °C | 59 °C | |
Low slope | <52 | <52 | 0.5 (0-3) | 0.6 (0-4) |
Mid-slope | <52 to 160 | <52 to 90 | 18.2 (1-52) | 16.8 (4-52) |
Ridge | <52 to >800 | <52 to >800 | 27.5 (9-55) | 24.0 (7-55) |
Pre- and postfire frequency, density, and basal area of canopy species on the ridge | ||||||
Ridge | Frequency (%) | Density (stems/ha) | Basal area (m²/ha) | |||
Time since fire | prefire | 3 mo | prefire | 3 mo | prefire | 3 mo |
American chestnut | 21 | 0 | 29 | 0 | 0.11 | 0 |
blackgum | 14 | 0 | 29 | 0 | 0.17 | 0 |
black locust | 7 | 0 | 7 | 0 | 0.01 | 0 |
Carolina silverbell | 7 | 7 | 7 | 7 | 0.15 | 0.15 |
chestnut oak | 93 | 64 | 239 | 146 | 5.22 | 3.33 |
common serviceberry | 43 | 21 | 109 | 70 | 0.97 | 0.67 |
eastern hemlock | 7 | 0 | 7 | 0 | 0.26 | 0 |
hickory | 36 | 21 | 128 | 50 | 1.38 | 0.80 |
northern red oak | 21 | 14 | 17 | 14 | 0.07 | 0.07 |
pitch pine | 93 | 78 | 637 | 441 | 12.45 | 9.67 |
red maple | 50 | 21 | 108 | 41 | 2.14 | 1.21 |
sassafras | 7 | 0 | 3 | 0 | 0.01 | 0 |
scarlet oak | 57 | 36 | 121 | 60 | 2.26 | 1.55 |
sourwood | 50 | 50 | 96 | 77 | 1.60 | 1.40 |
white oak | 7 | 7 | 7 | 7 | 0.02 | 0.02 |
Total | 1,545a* | 913b | 26.84a | 18.86b | ||
*Values with the same letters are not significantly different (P≤0.05) between time periods. |
The average percent mortality following the fire ranged from 18.5% to 30.6% for the dominant overstory species (pitch pine, chestnut oak, and scarlet oak). For associated overstory species, mortality ranged from 25.0% to 100%.
Average mortality of overstory species on burned ridge | |||
Species | N | Mortality (%) | SE |
American chestnut | 3 | 100 | 0 |
chestnut oak | 12 | 30.6 | 13.3 |
common serviceberry | 4 | 25.0 | 25.0 |
hickory | 5 | 57.5 | 17.5 |
pitch pine | 12 | 18.5 | 8.6 |
red maple | 7 | 42.8 | 20.2 |
scarlet oak | 8 | 29.2 | 16.0 |
Total density and basal area of understory vegetation on the ridge was significantly (P≤0.05) lower following the fire. However, total density and basal area increased with increased time since fire, although basal area and density had not recovered to prefire levels within a year of the fire. Mountain-laurel density and basal area were significantly (P≤0.05) lower after burning. Pitch pine understory density increased after the first postfire year. Black locust, chestnut oak, and scarlet oak densities were significantly (P≤0.05) greater after the ridge burned. White oak, northern red oak, and black oak were not present in the understory after the fire.
Pre- and postfire frequency, density, and basal area of understory species on the ridge | |||||||||
Ridge | Frequency (%) | Density (stems/ha) | Basal area (m²/ha) | ||||||
Time since fire | prefire | 3 mo | 1 yr, 3 mo | prefire | 3 mo | 1 yr, 3 mo | prefire | 3 mo | 1 yr, 3 mo |
Understory species (≥1 cm basal diameter, <5 cm DBH) | |||||||||
American chestnut | 21 | 0 | 21 | 952 | 0 | 413 | 0.536 | 0 | 0.184 |
black locust | 14 | 0 | 28 | 10b* | 0 | 813a | 0.002 | 0 | 0.119 |
black oak | 36 | 0 | 0 | 19 | 0 | 0 | 0.010 | 0 | 0 |
chestnut oak | 50 | 14 | 21 | 505b | 25c | 720a | 0.244 | 0.024 | 0.097 |
deerberry | 0 | 0 | 7 | 0 | 0 | 317 | 0 | 0 | 0.025 |
common serviceberry | 36 | 7 | 7 | 76a | 6b | 3b | 0.027 | 0.008 | 0.001 |
flame azalea | 7 | 0 | 7 | 159a | 0 | 19b | 0.038 | 0 | 0.002 |
hickory | 14 | 0 | 14 | 82 | 0 | 161 | 0.022 | 0 | 0.025 |
mountain-laurel | 100 | 21 | 14 | 8,651a | 248b | 168b | 4.97a | 0.127b | 0.403b |
northern red oak | 36 | 0 | 0 | 368a | 19b | 0 | 0.187 | 0.002 | 0 |
pitch pine | 21 | 0 | 7 | 165 | 0 | 317 | 0.212 | 0 | 0.035 |
red maple | 43 | 14 | 14 | 168 | 13 | 82 | 0.045 | 0.010 | 0.011 |
sassafras | 36 | 7 | 36 | 321b | 82c | 571a | 0.050 | 0.191 | 0.102 |
scarlet oak | 50 | 7 | 50 | 295b | 6c | 1,997a | 0.078b | 0.008b | 0.222a |
sourwood | 7 | 0 | 14 | 10 | 10 | 29 | 0.001 | 0.001 | 0.004 |
sweet birch | 0 | 0 | 7 | 0 | 0 | 79 | 0 | 0 | 0.006 |
white oak | 28 | 0 | 0 | 397 | 0 | 0 | 0.096 | 0 | 0 |
Total | 12,178a | 409c | 5,692b | 6.522a | 0.371c | 1.236b | |||
*Values with the same letters are not significantly different (P≤0.05) between time periods. |
The number of pitch pine seedlings increased by 358% in the third postfire month but was 35% of the prefire number a year following the fire. Common serviceberry seedlings increased by 350% a year after the fire.
The coverage of ground layer vegetation on the ridge slightly exceeded prefire levels by the first postfire year. Black oak, white oak, sourwood, and black locust were present in the prefire surface layer but were not present a year after the fire. Red maple, chestnut oak, and sassafras had greater cover after than before the fire. Blueberry, buffalo nut, mountain sweetpepperbush, and flame azalea all had greater than prefire cover levels 1 year after the fire. Pitch pine, present with low cover in prefire vegetation, was absent from the ground layer after the fire. Most herbs and vines present in the prefire community had increased cover in the first postfire year. Sedge and goldenrod species present in the prefire community, however, were absent from the community a year after fire. Bedstraw, western brackenfern, greater tickseed, common goldstar, bellwort, Michaux's saxifrage, New York fern, plains snakecotton, little bluestem, and panicgrass were only found on the ridge after the fire.
Pre- and postfire cover of herb-layer vegetation on the ridge | |||
Time since fire | Prefire | 3 mo | 1 year, 3 mo |
Ground layer species | |||
Trees | cover (%) | ||
American chestnut | 0 | 0.7 | 0 |
black locust | 0.02 | 0.5 | 0 |
black oak | 0.06 | 0.08 | 0 |
chestnut oak | 0.25 | 0.10 | 1.29 |
common serviceberry | 0.06 | 0.08 | 0.08 |
northern red oak | 0.08 | 0.08 | 0.25 |
pitch pine | 0.10 | 0.08 | 0 |
red maple | 0.25 | 0.08 | 1.17 |
sassafras | 0.10 | 0.25 | 2.88 |
scarlet oak | 0.08 | 0.03 | 0.21 |
sourwood | 0.02 | 0.5 | 0 |
white oak | 0.03 | 0 | 0 |
Shrubs | |||
blackberry | 0 | 0 | 0.12 |
black huckleberry | 1.03 | 1.88 | 0.96 |
blueberry | 2.28 | 2.28 | 5.17 |
buffalo nut | 0.18 | 0.08 | 0.67 |
flame azalea | 0.02 | 0.25 | 1.46 |
mountain-laurel (clone density = #/ha) |
28.0 | 3.67 (11,307) |
11.4 (9,285) |
mountain sweetpepperbush | 0.07 | 0.03 | 0.96 |
smooth sumac | 0 | 0.03 | 0 |
Forbs | |||
bedstraw | 0 | 0.13 | 1.33 |
bellwort | 0 | 0.03 | 0 |
common goldstar | 0 | 0.05 | 0 |
beetleweed | 0.40 | 0.10 | 0.92 |
greater tickseed | 0 | 0.05 | 0 |
goldenrod | 0.02 | 0 | 0 |
Indian cucumber | 0.02 | 0 | 0.12 |
Michaux's saxifrage | 0 | 0.02 | 0.29 |
narrowleaf cowwheat | 0.22 | 0.02 | 1.17 |
New York fern | 0 | 0.02 | 0 |
plains snakecotton | 0 | 0 | 0.12 |
trailing arbutus | 0.55 | 0.10 | 0.33 |
western brackenfern | 0 | 0.10 | 0.42 |
Graminoids | |||
little bluestem | 0 | 0.23 | 0.54 |
panicgrass | 0 | 0 | 2.75 |
sedge | 1.08 | 0.10 | 0 |
Vines | |||
greenbrier | 0.63 | 0.40 | 2.71 |
Total | 35.610.6 | 37.7 | |
Species richness | 24 | 33 | 26 |
Pielou evenness index | 0.32 | 0.61 | 0.77 |
The fire at the midslope position was less severe than that at the ridge. Total pre- and postfire overstory density and basal area were not significantly (P≤0.05) different, and pre- and postfire differences in individual overstory species frequency, density, and basal area were little to none.
Pre- and postfire frequency, density, and basal area of overstory species at the midslope position | ||||||
Frequency (%) | Density (stems/ha) | Basal area (m²/ha) | ||||
Time since fire | prefire | 3 mo | prefire | 3 mo | prefire | 3 mo |
blackgum | 22 | 22 | 156 | 156 | 0.99 | 0.99 |
black locust | 56 | 44 | 89 | 64 | 0.66 | 0.53 |
Carolina silverbell | 11 | 11 | 44 | 33 | 0.26 | 0.23 |
chestnut oak | 56 | 44 | 99 | 94 | 6.47 | 6.44 |
cucumber-tree | 11 | 11 | 5 | 5 | 0.04 | 0.04 |
common serviceberry | 33 | 33 | 38 | 38 | 0.27 | 0.27 |
eastern hemlock | 22 | 22 | 22 | 22 | 0.94 | 0.94 |
hickory | 67 | 67 | 173 | 178 | 2.84 | 2.89 |
red maple | 200 | 100 | 626 | 606 | 9.01 | 9.02 |
scarlet oak | 22 | 22 | 38 | 27 | 4.00 | 3.91 |
sourwood | 67 | 67 | 153 | 137 | 3.16 | 3.11 |
sweet birch | 22 | 22 | 5 | 5 | 0.03 | 0.03 |
Total | 1,448a* | 1,365a | 28.69a | 28.42a | ||
*Values with the same letters are not significantly different (P≤0.05) between time periods. |
Total density and basal area of midslope vegetation was significantly (P≤0.05) reduced by the fire. Red maple, American chestnut, mountain-laurel, and sourwood had significantly (P≤0.05) lower density and basal area after the fire. Hickory, Carolina silverbell, cucumber-tree, buffalo nut, white oak, black locust, and eastern hemlock were present in the prefire community but were not present 3 months after the fire. Rosebay, a dominant in the prefire understory, remained dominant after the fire with relatively little change in density or basal area after the fire.
Pre- and postfire frequency, density, and basal area of understory species at the midslope position | ||||||
Frequency (%) | Density (stems/ha) | Basal area (m²/ha) | ||||
Time since fire | prefire | 3 mo | prefire | 3 mo | prefire | 3 mo |
Understory species (≥1 cm basal diameter, <0.5 cm DBH) | ||||||
American chestnut | 44 | 11 | 573a* | 20b | 0.127a | 0.002b |
blackgum | 11 | 11 | 123a | 10b | 0.012a | 0.012a |
black locust | 11 | 0 | 15 | 0 | 0.008 | 0 |
buffalo nut | 11 | 0 | 123 | 0 | 0.047 | 0 |
Carolina silverbell | 22 | 0 | 494 | 0 | 0.064 | 0 |
chestnut oak | 11 | 11 | 25 | 5 | 0.012 | <0.001 |
cucumber-tree | 11 | 0 | 123 | 0 | 0.019 | 0 |
eastern hemlock | 11 | 0 | 10 | 0 | 0.002 | 0 |
hickory | 11 | 0 | 5 | 0 | 0.006 | 0 |
mountain-laurel | 67 | 11 | 4,691a | 123b | 4.497a | 0.422b |
northern red oak | 22 | 0 | 20 | 0 | 0.010 | 0 |
red maple | 56 | 22 | 326a | 15b | 0.494a | 0.019a |
rosebay | 22 | 11 | 1,605a | 1,358a | 7.231a | 7.789a |
sourwood | 22 | 11 | 138a | 25b | 0.015a | 0.002b |
white oak | 22 | 0 | 247 | 0 | 0.020 | 0 |
Total | 8,518a | 1,556b | 12.56a | 8.25b | ||
*Values with the same letters are not significantly different (P≤0.05) between time periods. |
The fire at the low-slope position was less severe than that at the ridge or midslope. Total pre- and postfire canopy density and basal area were not significantly (P≤0.05) different, and pre- and postfire differences in individual species frequency, density, and basal area were little to none.
Pre- and postfire frequency, density, and basal area of overstory species at the low-slope position | ||||||
Frequency (%) | Density (stems/ha) | Basal area (m²/ha) | ||||
Time since fire | prefire | 3 mo | prefire | 3 mo | prefire | 3 mo |
American chestnut | 11 | 11 | 11 | 11 | 0.001 | 0.001 |
American witchhazel | 11 | 11 | 11 | 11 | 0.02 | 0.02 |
blackgum | 11 | 11 | 22 | 22 | 0.07 | 0.07 |
black locust | 22 | 22 | 22 | 22 | 0.94 | 0.94 |
Carolina silverbell | 22 | 11 | 44 | 15 | 0.13 | 0.05 |
chestnut oak | 33 | 33 | 32 | 32 | 0.63 | 0.62 |
cucumber-tree | 11 | 11 | 30 | 39 | 0.16 | 0.18 |
common serviceberry | 44 | 33 | 47 | 37 | 0.28 | 0.24 |
eastern hemlock | 89 | 89 | 238 | 243 | 3.80 | 3.87 |
hickory | 78 | 78 | 186 | 167 | 6.64 | 6.62 |
northern red oak | 33 | 33 | 21 | 21 | 0.61 | 0.63 |
red maple | 89 | 89 | 333 | 328 | 6.54 | 6.59 |
sassafras | 11 | 11 | 5 | 5 | 0.07 | 0.07 |
scarlet oak | 33 | 33 | 21 | 21 | 3.12 | 3.16 |
sugar maple | 11 | 11 | 5 | 5 | 0.04 | 0.04 |
sourwood | 11 | 11 | 22 | 22 | 0.78 | 0.78 |
striped maple | 44 | 44 | 64 | 64 | 0.49 | 0.50 |
white oak | 22 | 22 | 36 | 36 | 2.88 | 2.90 |
tuliptree | 22 | 22 | 15 | 15 | 0.48 | 0.51 |
Total | 1,167a* | 1,117a | 27.72a | 27.82a | ||
*Values with the same letters are not significantly different (P≤0.05) between time periods. |
The low-severity fire at the low slope increased total understory stem density, though not significantly. Hawthorn, which was not present before the fire, had a density of 123 stems/ha 3 months after the fire. Postfire densities of American chestnut, white ash, Carolina silverbell, and buffalo nut were more than double the prefire densities 3 months after spring burning. Densities of flame azalea, eastern hemlock, northern red oak, and hickory decreased by more than half, and mountain magnolia and chestnut oak were absent after the fire.
Pre- and postfire frequency, density, and basal area of canopy species at the low-slope position. | ||||||
Frequency (%) | Density (stems/ha) | Basal area (m²/ha) | ||||
Time since fire | prefire | 3 mo | prefire | 3 mo | prefire | 3 mo |
Understory species (≥1 cm basal diameter, <0.5 cm DBH) | ||||||
American chestnut | 33 | 44 | 138 | 592 | 0.044 | 0.115 |
buffalo nut | 11 | 33 | 123 | 370 | 0.051 | 0.135 |
Carolina silverbell | 33 | 33 | 59 | 138 | 0.022 | 0.031 |
chestnut oak | 11 | 0 | 5 | 0 | <0.001 | 0 |
cucumber-tree | 33 | 44 | 207 | 301 | 0.056 | 0.074 |
common serviceberry | 33 | 22 | 30 | 54 | 0.016 | 0.037 |
eastern hemlock | 22 | 22 | 143 | 20 | 0.400 | 0.019 |
flame azalea | 11 | 11 | 864 | 370 | 0.320 | 0.200 |
hawthorn | 0 | 11 | 0 | 123 | 0 | 0.014 |
hickory | 11 | 11 | 40 | 10 | 0.006 | 0.007 |
mountain magnolia | 11 | 0 | 5 | 0 | <0.001 | 0 |
northern red oak | 22 | 22 | 133 | 64 | 0.026 | 0.005 |
red maple | 22 | 22 | 30 | 44 | 0.010 | 0.021 |
sugar maple | 33 | 33 | 138 | 158 | 0.026 | 0.032 |
striped maple | 22 | 22 | 133 | 153 | 0.018 | 0.026 |
sourwood | 11 | 11 | 5 | 10 | 0.002 | <0.001 |
sweet birch | 11 | 11 | 5 | 10 | <0.001 | <0.001 |
white ash | 11 | 22 | 15 | 79 | 0.005 | 0.017 |
white oak | 22 | 11 | 10 | 34 | 0.001 | 0.003 |
tuliptree | 22 | 33 | 69 | 118 | 0.011 | 0.020 |
Total | 2,153a* | 2,652a | 1.015a | 0.758a | ||
*Values with the same letters are not significantly different (P≤0.05) between time periods. |
Common name | Scientific name |
striped maple | Acer pensylvanicum |
red maple | Acer rubrum |
sugar maple | Acer saccharum |
common serviceberry | Amelanchier arborea |
sweet birch | Betula lenta |
sedge | Carex spp. |
hickory | Carya spp. |
American chestnut | Castanea dentata |
mountain sweetpepperbush | Clethra acuminata |
greater tickseed | Coreopsis major |
hawthorn | Crataegus spp. |
trailing arbutus | Epigaea repens |
white ash | Fraxinus americana |
plains snakecotton | Froelichia floridana |
beetleweed | Galax urceolata |
bedstraw | Galium spp. |
black huckleberry | Gaylussacia baccata |
Carolina silverbell | Halesia carolina |
American witchhazel | Hamamelis virginiana |
common goldstar | Hypoxis hirsuta |
mountain-laurel | Kalmia latifolia |
tuliptree | Liriodendron tulipifera |
cucumber-tree | Magnolia acuminata |
mountain magnolia | Magnolia fraseri |
Indian cucumber | Medeola virginiana |
narrowleaf cowwheat | Melampyrum lineare |
blackgum | Nyssa sylvatica |
sourwood | Oxydendrum arboreum |
panicgrass | Panicum spp. |
pitch pine | Pinus rigida |
western brackenfern | Pteridium aquilinum |
buffalo nut | Pyrularia pubera |
white oak | Quercus alba |
scarlet oak | Quercus coccinea |
chestnut oak | Quercus prinus |
northern red oak | Quercus rubra |
black oak | Quercus velutina |
smooth sumac | Rhus glabra |
flame azalea | Rhododendron calendulaceum |
rosebay | Rhododendron maximum |
black locust | Robinia pseudoacacia |
blackberry | Rubus spp. |
sassafras | Sassafras albidum |
Michaux's saxifrage | Saxifraga michauxii |
little bluestem | Schizachyrium scoparium |
greenbrier | Smilax spp. |
goldenrod | Solidago spp. |
New York fern | Thelypteris noveboracensis |
eastern hemlock | Tsuga canadensis |
bellwort | Uvularia spp. |
deerberry | Vaccinium stamineum |
blueberry | Vaccinium spp. |
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2. Hann, Wendel; Havlina, Doug; Shlisky, Ayn; [and others]. 2005. Interagency fire regime condition class guidebook. Version 1.2, [Online]. In: Interagency fire regime condition class website. U.S. Department of Agriculture, Forest Service; U.S. Department of the Interior; The Nature Conservancy; Systems for Environmental Management (Producer). Variously paginated [+ appendices]. Available: http://www.frcc.gov/docs/1.2.2.2/Complete_Guidebook_V1.2.pdf [2007, May 23]. [66734]
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4. LANDFIRE Rapid Assessment. 2007. Rapid assessment reference condition models. In: LANDFIRE. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Lab; U.S. Geological Survey; The Nature Conservancy (Producers). Available: http://www.landfire.gov/models_EW.php [66533]
5. Vose, James M.; Swank, Wayne T.; Clinton, Barton D.; Knoepp, Jennifer D.; Swift, Lloyd W. 1999. Using stand replacement fires to restore southern Appalachian pine-hardwood ecosystems: effects on mass, carbon, and nutrient pools. Forest Ecology and Management. 114(2-3): 215-226. [30149]