Wildlife, Animals, and Plants
|
|
FIRE EFFECTS
SPECIES: Artemisia frigida | Fringed Sagebrush
IMMEDIATE FIRE EFFECT ON PLANT :
Limited evidence suggests that specific fire effects may vary according
to fire intensity and severity or season of burn. Ecotypic differences
may also exist. Fringed sagebrush may be killed or seriously damaged by
fire when aboveground foliage is consumed [4]. In southern British
Columbia, fringed sagebrush growing in big sagebrush stands was killed
when these stands were burned prior to spring greenup.
In some locations, individual plants can survive even when aboveground
vegetation is removed. Sprouting has been reported in southern British
Columbia, east-central Alberta, and elsewhere [1,13]. Effects of fire
are minimized where fringed sagebrush sprouts readily.
DISCUSSION AND QUALIFICATION OF FIRE EFFECT :
NO-ENTRY
PLANT RESPONSE TO FIRE :
The response of fringed sagebrush to fire is highly variable. Community
composition, site characteristics, prior grazing history, fire
intensity, and timing of burn influence response. Little is known about
the time required for fringed sagebrush to reoccupy a site. Fringed
sagebrush typically reestablishes a burned site either from on-site
surviving seed stored in the soil or seed dispersed from off-site.
Plants grown from seed may require up to 3 years to reach sexual
maturity on particularly harsh sites. Specific recovery time from seed
following fire in fringed sagebrush communities has not been documented.
Under some circumstances, fringed sagebrush can regenerate vegetatively
and quickly reoccupy a site [1,13]. Stump sprouting or suckering has
been observed in British Columbia and in Alberta [1,13]. Wright and
others [88] describe fringed sagebrush as a "weak sprouter." Sprouting
is probably much more likely following burns of low intensity and
severity.
General trends following fire in a particular season have been difficult
to discern, indicating that other factors must also be considered when
projecting the fire response of fringed sagebrush. Dix [25] reported an
increased frequency of fringed sagebrush after summer fires in western
North Dakota grasslands, whereas Mitchell [50] reported decreases after
a July fire in a western Montana grassland. Decreases in frequency or
cover were noted following spring and fall fires in North Dakota and
Canada [5,25] and after a spring fire in western Montana [2]. Wright
and Bailey [79] reported that fringed sagebrush is generally reduced by
spring fires in mixed-grass prairies in the northern Great Plains.
However, Anderson and Bailey [1] observed increases in fringed sagebrush
following annual early spring fires of low intensity in east-central
Alberta. Increases in both the density and biomass of fringed sagebrush
were noted after a spring fire in Wind Cave National Park, South Dakota
[27]. Other researchers in the northern Great Plains report little
change in fringed sagebrush cover after fire [41]. Clearly, more
research is needed to fully document the response of fringed sagebrush
to fire and to account for the different responses noted.
DISCUSSION AND QUALIFICATION OF PLANT RESPONSE :
Season of burn, fire intensity, site characteristics, plant
associations, and geographic and climatic factors all influence the way
in which fringed sagebrush responds to fire. Both increases and
decreases in fringed sagebrush cover or frequency has been noted after
spring and summer fires. The following research results demonstrate the
variable response of fringed sagebrush to fire (Study locations, general
habitat, and fire intensity are given when such information was noted):
- western North Dakota grasslands [25]
frequency index values
summer burn fall burn spring burn
unburned burned unburned burned unburned burned
15 25 17 7 42 10
-------------------------------------------------------------------------
- western Montana grasslands - spring burn 1977 [2]
average % cover on burned and unburned stands
autumn 1977 spring 1978 summer 1978
unburned burned unburned burned unburned burned
0.1 + 0.2 0.1 0.5 0.1
--------------------------------------------------------------------------
- east-central Alberta - aspen parkland - low intensity spring burn [1]
frequency (%) canopy cover (%)
unburned burned unburned burned
3 7 0.2 0.3
---------------------------------------------------------------------------
- British Columbia - mountain rangelands (% cover fringed sagebrush) [65]
burned subalpine unburned subalpine spruce-willow alpine
slopes clearings birch
3 0 0 0
-----------------------------------------------------------------------------
Wind Cave National Park, South Dakota - grasslands - spring burn [27]
ground cover (%) -
control 1981 burn
1980 1981 1982 1983 1980 1981 1982 1983
site1 1.8 2.5 4.5 5.3 2.8 1.8 2.2 7.6
site2 1.1 1.1 3.0 5.3 1.1 0.3 0.3 0.4
frequency (%) -
site1 27.4 28.2 21.4 37.3 30.6 21.0 21.4 53.2
site2 18.3 12.7 10.3 21.4 16.3 5.6 3.2 3.2
density (avg. # of stems per quadrat)
biomass (grams)
control 1981 burn
density biomass density biomass
1982 1983 1982 1983 1982 1983 1982 1983
site1 1.5 2.2 3.80 3.28 1.1 2.4 2.98 3.00
site2 0.7 0.9 2.79 2.06 0.1 0.1 0.32 0.12
---------------------------------------------------------------------------
western Montana -grasslands [50]
burned area unburned area
cover frequency cover frequency
1st year 0.4 3 4.2 33
FIRE MANAGEMENT CONSIDERATIONS :
NO-ENTRY
Related categories for Species: Artemisia frigida
| Fringed Sagebrush
|
|