Wildlife, Animals, and Plants
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FIRE CASE STUDIES
SPECIES: Quercus emoryi | Emory Oak
CASE NAME :
Lyle Canyon Prescribed Fire, Arizona (Emory oak)
SEASON/SEVERITY CLASSIFICATION :
spring fire/low- to moderate-severity
STUDY LOCATION :
The study was conducted at the National Audubon Appleton-Whittel
Research Sanctuary in foothills on the west side of the Huachuca
Mountains of Arizona. The research focused on two areas: a grassland
and a Madrean evergreen woodland. This case study presents only the
Madrean evergreen woodland results since Emory oak (Quercus emoryi) did
not occur in the grassland. Study plots were located in Lyle Canyon,
which is leased by the Sanctuary from the Coronado National Forest.
PREFIRE VEGETATIVE COMMUNITY :
Lyle Canyon is covered by a Madrean evergreen oak woodland. The
overstory consisted of Emory oak and Arizona white oak. The burn
treatment study plots had a total of 20 Emory oak and 15 Arizona white
oak; control plots had a total of 20 Emory oak and 10 Arizona white oak.
Common understory shrubs were wait-a-minute bush (Mimosa biuncifera),
velvet-pod mimosa (M. dysocarpa), and yerba de pasmo (Baccharis
pteronioides). Grasses and forbs most commonly present were sideoats
grama (Bouteloua curtipendula), plains lovegrass (Eragrostis
intermedia), annual goldeneye (Viguiera annua), and Arizona poppy
(Kallstroemia parviflora).
TARGET SPECIES PHENOLOGICAL STATE :
The phenological stages of the plants were not specifically mentioned.
At the time of burning in May, Emory oak would be past flowering, and
fruits would be developing.
SITE DESCRIPTION :
The study site was located in a steep-sided canyon at 4,922 feet (1,500
m) elevation. Spring months are dry and warm in this semiarid climate.
The average annual precipitation is 16.9 inches (430 mm) and occurs
bimodally. No information was given on specific topography, slope, or
soils.
FIRE DESCRIPTION :
Ten plots, 65.6 by 98.4 feet (20x30 m), were assigned either to burn or
control treatments. Plots were paired for physiognomy and vegetation.
Twenty quadrats, 7.9 by 19.7 inches (20x50 cm), were located in each
plot for a total of 200 quadrats. The fire burned between 10 a.m. and
12 m. on 25 May 1984. Air temperature was from 90 to 92 degrees
Fahrenheit (32-33 deg C). The relative humidity ranged from 16 to 18
percent. Winds were variable and gusted from 5 to 10 mph (8.1-16.1
km/h). Dead fine fuel moistures were between 5 and 6 percent.
Fires moved slowly (1.6 to 4.9 feet per minute [0.5-1.5 m/min]) with
flame lengths of 0.7 to 1.6 feet (0.2-0.5 m) in four of the five burn
plots. This was a heat release of 2.3 to 16.8 Btu per second per foot
(8-58 kw/s/m). The fire moved rapidly (98.4 feet per minute [30 m/min])
with a heat release of 75.2 Btu per second per foot (260 kw/s/m) over
the remaining burn plot.
FIRE EFFECTS ON TARGET SPECIES :
Mature Emory oak were not affected by the fire [12]. Postfire
vegetation was sampled during two growing seasons in 1984 and 1985.
There was no significant (P>0.05) difference in numbers of Emory oak
seedlings on the burn plots compared to the controls.
FIRE MANAGEMENT IMPLICATIONS :
Fire is a part of the historic Madrean evergreen woodland [125]. This
prescribed fire did not have any lasting effects on woody vegetation in
the study area. Burning had little detectable effect on the seedlings
of Emory oak. This is probably due to the short duration and low heat
released by the fires.
Related categories for Species: Quercus emoryi
| Emory Oak
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