More info for the terms:
cool-season,
cover,
density,
fire frequency,
frequency,
habitat type,
prescribed fireKentucky bluegrass's fire response varies greatly depending on season of
burning, fire frequency, and postfire precipitation and soil moisture.
Season of burning: Kentucky bluegrass postfire cover, biomass, and
flower stalk density are often greatly reduced during the first postfire
growing season by a single late spring fire. Three examples are
presented to demonstrate rather typical first-year responses to late
spring burning: (1) in mixed-grass prairie unburned for several years in
north-central Nebraska, a single prescribed fire in mid-April or mid-May
greatly reduced Kentucky bluegrass basal cover in October, with cover on
burned plots only half that found on unburned plots [
83], (2) after a
single mid-April fire on a tallgrass prairie site unburned for several
years in Iowa, Kentucky bluegrass relative biomass decreased from 80
percent to 25 percent during the first postfire growing season [
53], and
(3) in the mountains of western Montana, Kentucky bluegrass frequency
was reduced 27.5 percent by a single late May fire in a
sagebrush/bunchgrass habitat type [
18].
Kentucky bluegrass biomass production and density may be unaffected or
increase after burning at other times of the year, such as early spring,
summer, or fall. It consistently recovers more quickly from burning at
these times of year than from burning in late spring.
In fields dominated by cool-season grasses in Wisconsin, Kentucky
bluegrass was reduced to one-fifth of its original density after 6 years
of annual burning in May; annual burning in March or October did not
affect Kentucky bluegrass density [
23]. A different study in Wisconsin
showed that flower stalk density was reduced 70 percent by three annual
mid-May prescribed fires but was slightly increased by annual burning in
late March or early April [
51]. Although summer grass fires can be
relatively intense, Kentucky bluegrass is dormant at this time. It may
not be harmed by summer burning, and if precipitation is favorable, it
may even increase. In mixed-grass prairie in north-central South
Dakota, Kentucky bluegrass frequency increased or remained unchanged on
uplands burned in early August followed by a wet spring, but decreased
on uplands burned in summer following a dry spring [
103,
104]. Kentucky
bluegrass's density tripled 1 year after late October and early November
low-intensity prescribed fires in aspen stands in Colorado [
99]. In
ponderosa pine habitat types in British Columbia, Kentucky bluegrass
biomass was unchanged by an October prescribed fire [
110].
Fire frequency: Even after late spring burning, unless burned a second
time, Kentucky bluegrass density and cover often return to prefire
levels within 1 to 3 years. For example, burning in May or June in Wind
Cave National Park, South Dakota, consistently reduced Kentucky
bluegrass canopy coverage, height, shoot density, flower stalk density,
and biomass during the first postfire growing season but not during
postfire years 2 and 3 [
87]. In fact, biomass and density were often
greater on burned plots than on control plots during postfire year 2.
Other studies in mixed-grass prairie have shown Kentucky bluegrass cover
can be reduced for 2 or 3 years by a single late spring fire [
34,
83,
94].
Kentucky bluegrass cannot withstand frequent spring burning. In the
tallgrass prairie, its density decreases with increased fire frequency,
and it may be eliminated from sites that are burned annually for several
years [
1,
5,
28,
44,
65,
77]. In the Flint Hills of northeastern Kansas,
Kentucky bluegrass canopy coverage under different burning regimes was
30.3 percent on an area unburned for 11 years, 7.0 percent on an area
burned 1 and 5 years before sampling, and 0 percent on an area burned
annually for 5 years [
1]. A similar response was observed on a
reconstructed tallgrass prairie in Illinois subjected to the following
burning treatments [
44]:
not burned = unburned for 19 years
burned twice = burned Feb. 28, 1952 and April 16, 1959
burned three times = burned Feb. 28, 1952; April 16, 1959; and May 2, 1961
burned four times = burned Feb. 28, 1952; April 16, 1959; May 2, 1961; and
May 10, 1962
Sampling at the end of the 1962 growing season showed the relative
percentage of bluegrass (P. compressa and P. pratensis) shoot biomass
decreased with increased burning frequency in two community types as
follows:
Burning Treatment
not burned burned twice burned burned
3 times 4 times
Community type
big bluestem 23.4 18.3 4.6 0
indiangrass 18.6 15.9 3.3 0
Vogl [
117] sampled several pine barrens in northern Wisconsin and
reported that Kentucky bluegrass frequency either increased or decreased
within 1 year of a single spring fire but that Kentucky bluegrass was
eliminated on sites spring burned more than once every few years.
Influence of postfire moisture: Kentucky bluegrass is more susceptible
to fire damage on ridge sites than in depressions, especially in dry
years [
52]. In fact, in swales and low prairie sites that receive
upslope moisture, Kentucky bluegrass often increases after spring
burning. In bluegrass fields in Wisconsin, Kentucky bluegrass density
and biomass increased in depressions but decreased or remained unchanged
on ridgetops after two successive mid-April fires [
129]. In eastern
South Dakota, Kentucky bluegrass recovered well from early May burning
if irrigated. On burned but unirrigated plots, however, biomass
decreased sharply [
12]. In eastern North Dakota, lowland and upland
prairies were burned on May 8, 1966. Postfire data on August 4, 1966
showed that Kentucky bluegrass frequency increased on lowlands but
remained unchanged on uplands. Biomass on both uplands and lowlands
decreased, but the decrease was much greater on uplands [
43]. When
postfire growing season precipitation was "considerably below normal" in
Wind Cave National Park, South Dakota, Kentucky bluegrass biomass on
burned areas was less than half that found on unburned areas whether
burned on September 18, February 13, or April 10 [
37].
In a sagebrush/rough fescue habitat type in Montana, Kentucky bluegrass
biomass increased the first summer after a mid-May prescribed fire [
95].
This increase was unexpected because bluegrass should be susceptible to
burning at this time. This increase may be due to the high moisture
availability in surface soils at this site due to concave slope shape.
In contrast, another study in western Montana found Kentucky bluegrass
decreased after a prescribed fire on May 24 in a sagebrush/fescue
habitat type [
18].