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Wildlife, Animals, and Plants
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FIRE EFFECTS
SPECIES: Typha latifolia | Common Cattail
IMMEDIATE FIRE EFFECT ON PLANT :
The effects of fire on common cattail vary with water depth and soil
moisture. On flooded sites and on sites with exposed but saturated
soils, fire consumes most or all of the aboveground biomass, but
underground rhizomes remain undamaged and plants survive [11,41]. When
soils become dry because of drought or marshland drainage, fires can
burn deep into the organic horizons, consuming the rhizomes and killing
the plant [43].
DISCUSSION AND QUALIFICATION OF FIRE EFFECT :
NO-ENTRY
PLANT RESPONSE TO FIRE :
Common cattail quickly sprouts from surviving rhizomes following fires
that remove the top-growth. If burned when plants are dormant, new
top-growth is initiated in the spring, and annual productivity is not
lowered [40,41]. Even following summer fires, plants quickly initiate
new growth from surviving underground rhizomes and grow until killed by
fall frosts. After an early September fire in Utah, common cattail grew
to 1.3 feet (0.4 m) in height before winter dormancy [41].
Hybrid cattail (T. X glauca) stands in New Brunswick, Canada, were
burned in spring, summer, or fall in both flooded and drained marshes.
Summer burning on drained sites resulted in the greatest reductions in
cover, density, and height 3 years after burning. Three years after
burning on flooded marsh, hybrid cattail increased in cover but showed
little or no change in cover, stem density, or height. Changes in these
characteristics 3 years after burning are presented below [24]:
control spring summer autumn
burned burned burned
cover (%)
drained marsh 56 54 36 48
flooded marsh 41 44 55 46
stem density/m2
drained marsh 15 14 9 12
flooded marsh 10 10 12 10
plant height (cm)
drained marsh 133 126 111 130
flooded marsh 155 165 158 156
DISCUSSION AND QUALIFICATION OF PLANT RESPONSE :
NO-ENTRY
FIRE MANAGEMENT CONSIDERATIONS :
Prescribed burning in late fall, winter, or early spring when plant tops
are dry opens up common cattail stands by removing years of accumulated
litter. In northern latitudes, winter burning has advantages in that
fires can be better directed over ice than open water, as the ice allows
for faster movement of men and equipment. Additionally, winter fires
are easier to control because they are of lower intensity than fires
during warmer months [1]. Annual burning is difficult because more than
1 year of litter is needed to carry fire in cattail stands [1,3].
On marshes where water levels can be controlled, drawdown followed by
burning and rapid reflooding kills common cattail if regrowth is kept
completely submerged. Following marsh drawdown and burning in Utah,
common cattail quickly resprouted and covered areas that were reflooded
with up to 8 inches (20 cm) of water. No plants survived, however, on
areas flooded with 8 to 18 inches (20-46 cm) of water [32]. When winter
burning over ice in southwestern Ontario, Ball [1] found that
slow-moving backfires left the shortest cattail stubble which
subsequently needed the least amount of water level increase to submerge
the stalks. Furthermore, snow buildup over ice can protect the stalks
from burning, resulting in tall stubble that is difficult to submerge
the following spring. Thus, when using winter burning in conjunction
with water level manipulation to control cattail, it is best to burn
over ice in early winter before snow accumulation or in early spring
after snow melt.
In Utah, common cattail was controlled with a combination of burning and
cutting. Stands were first cut, then the cut material burned. This
made it easier to flood the cut stems, and allowed a second cutting, if
needed, to be made very close to the ground [32].
In the Southern High Plains region of Texas, winter burning did not
improve common cattail nutritive quality [40].
Related categories for Species: Typha latifolia
| Common Cattail
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