Post Fire Livestock Management
Fire can have a dramatic
impact on rangeland forage. The magnitude of this impact is
dependant on numerous factors including plant species, season of the
fire, fire intensity, vigour of the plants prior to the fire,
associated species and climatic conditions during and following the
fire. Once rangeland has been burned, the range manager is faced
with numerous difficult choices including determining how long to
rest a particular pasture. This decision is often controversial but
very important since grazing management following burning has the
potential to significantly affect range health including
productivity and plant species composition.
WHY
REST?
Following a fire,
rangeland is often rested for the following reasons:
- To allow surviving plants to recover,
- To allow desirable plant species to regenerate, and
- To allow litter to accumulate.
Allowing
Plant Recovery
Some plants are
inherently more susceptible to fire than others. Bunchgrasses such
as Idaho fescue and needle-and-thread for example, are often more
vulnerable and are slower to recover than other grasses. Other less
dense bunchgrasses, such as bluebunch wheatgrass and various
rhizomatous grasses, such as pinegrass however, tend to be more
tolerant and generally only top-killed by fire. For the most part,
the impact of fire on British Columbia’s

ranges is dependant on
fire severity which is often correlated with season of burn. In
general, June and July fires are the most detrimental to
bunchgrasses, while July and August fires are the most detrimental
season to burn most forbs, shrubs and rhizomatous grasses (there are
notable exceptions including Kentucky bluegrass). The health of your
range prior to a fire also determines how long it will take range
plants to recover with unhealthy ranges generally taking longer to
recover than those healthy ranges. Finally, climate will also play
an integral role in range plant recovery. For example, below normal
precipitation in the years following a fire will typically prolong
the amount of time needed in order for your range to recover whereas
above average years may facilitate recovery.
Depending
on Burn Intensity Examples of Plant Recovery Time Are:
Pinegrass - will
generally recover in 1 year.
Bluejoint
-
will generally recover in 1 to 2 years.
Kentucky
Bluegrass - will
generally recover in 1 to 2 years.
Bluebunch
Wheatgrass - will
generally recover in 1 to 3 years.
Idaho
fescue - will
generally recover in 2 or more years.
Rough Fescue - will
generally recover in 2 or more years.
Tufted
Hairgrass - will
generally recover in 2 or more years.
Needlegrasses -
will generally recover in 3 or more years.
Beaked
Sedge - will
generally recover in 1 year.
Showy
Aster - will
generally recover in 1 year.
Willows - highly variable depending on species, varying from 1 to 5 years.
Red-osier
Dogwood - will
generally recover in 1 year.
Big Sage,
Antelope-bitterbrush - highly
variable, varying from 8 to 20 years.
Aspen
Poplar - will
generally recover in one year.
Note: These recovery
periods are all dependant on soil moisture, season and fire
severity.
Allowing
Desirable Plants to Regenerate
The initial concern for
range managers following a fire is to ensure that both plant vigour
and seed production is restored. Generally, range plants will
establish by either sprouting and/or from seed. Plants that
establish by re-sprouting usually deplete their energy
(carbohydrate) reserves and become especially vulnerable to further
damage. Even though these plants often appear to be highly
productive and nutritious, most will be in low vigour and thus
extremely vulnerable to grazing. If these plants are subjected to
grazing, some will be further weakened while others may be destroyed
and removed from the range plant community. Overall, it is important
for the range manager to ensure that the range is rested so that
carbohydrate reserves are replenished in the longer stem bases.
Fire often facilitates
seed production for a number of British Columbia species, including
bluebunch wheatgrass, pinegrass, and Junegrass. Depending on fire
severity, other species however, such as Idaho fescue, often show an
initial reduction in seed production (e.g., first two years). In
order for plant establishment from seed to occur, there must be a
source of viable seed, adequate seed coverage, suitable germination
temperatures, minimal competition form other plants and most
importantly, adequate soil moisture for the seedling to develop
sufficiently. In British Columbia’s southern interior, the last
requirement, adequate moisture, is often the most difficult one to
achieve. Once plants have been allowed to go to seed, livestock
grazing can be used to enhance the establishment of new plants
through promoting seed coverage and soil to seed contact.

Allowing
Litter to Accumulate
Most fires will consume a
majority of plant residue and litter. This is important since litter
is often required for both soil and watershed protection. For
example, a litter layer often performs the following ecological
functions:
-
Protects soil
against erosion (e.g., raindrop impact),
-
Detains
overland flow, and facilitates soil infiltration and permeability
-
Enhances
forage production, and
-
Buffers
against dry conditions by aiding moisture retention and reducing
moisture loss.
Therefore, in order to
promote these important ecological functions, post-fire livestock
management must promote the establishment of a litter layer.
DETERMINING
REST PERIOD
While most managers agree
with the principle of rangeland rest following a fire, the length of
rest is often a difficult and controversial decision, particularly
on Crown land. While this factsheet will not provide you with a
cookbook answer, it will discuss what to consider before restocking
the range. Most importantly, restocking decisions should vary from
one pasture to another and be made on a case-by-case basis since
plant recovery is often dependant on numerous site-specific
variables including those that affect plant survival, growth, and
reproduction. Once a restocking schedule has been established, it
must be flexible enough to account for situations that may impede
plant recovery, including below normal precipitation. In addition,
an inspection should be conducted prior to turning out on burned
pastures to ensure that the range is ready for grazing regardless of
whether the prescribed period of rest has been adhered to. In
general, when determining rest period, the following rules of thumb
should be considered:
- One
growing season of rest is often be adequate following a low
severity fire on range sites that were highly productive and
healthy prior to the fire.
- On
unhealthy range sites (e.g., perennial plants were low in vigour;
lots of invasive species) however, one growing season is often
inadequate for plant recovery.
- Bunchgrasses
often require longer rest periods and lighter utilization rates
than do other plants.
- Riparian
communities with shrubs and trees often require longer rest
periods.
- Rest
can also be adjusted depending on site objectives. For example,
some shrubs, such as antelope-bush, often require longer rest
periods whereas others, such as big sage, often benefit from
shorter rest periods. Also, depending on the site, grazing may
also be used to promote seed coverage and planting following
seed ripening, and reduce plant competition and thus facilitate
forest regeneration in cutblock situations.

POST
FIRE LIVESTOCK MANAGEMENT
Fire changes animal
behaviour by influencing grazing patterns, preferences, utilization
rates, and forage consumption. These changes are generally
attributed to changes in forage productivity, availability and
quality (see Factsheet 5)
and often cause wildlife and livestock to congregate on burned
areas. While this may be beneficial from an immediate animal
production standpoint, it may result in over-utilization of some
plants and thus become detrimental from a range health point of
view. Improved forage on burned sites can also cause animals to
avoid not burned areas. This combined with the removal of natural
barriers can result in a distribution problem and cause some areas
of a pasture to be over-utilized and others to be under-utilized.
Overall, in order to maximize use of the entire pasture and to limit
the overuse of individual plants, the range manager must overcome
these challenges by developing a range use plan that considers pre
and post range health, livestock type, stocking rate, distribution
tools, season of use, and intensity.
MONITORING
Since fire effects are often highly variable, it is important for the
range manager to monitor their range. Monitoring in both the short
and long-term allows evaluation of post-fire management and helps us
to understand the impacts of fire and grazing on range productivity
and sustainability. Monitoring and responding to observations early
on will assist us in maintaining productivity and sustainability
over the long term.
REFERENCES
National
Wildfire Coordinating Group. 2001. Fire Effects Guide. Available
online: http://www.nwcg.gov/pms/RxFire/FEG.pdf.
313 p.
Sanders,
K.D. 2000. How long should rangelands be rested from livestock
gazing following a fire? University of Idaho. Available online: http://www.cnr.uidaho.edu/range/publications/fire.pdf.
(4p).
Fire
Effects on Rangeland Factsheet Series
A
Fire Effects on Rangeland Factsheet series has been developed to
assist you in assessing and managing rangeland affected by fire. The
titles of these factsheets are:
1. Fire
Effects on Rangeland Ecosystems
2. Fire
Effects on Soils
3. Fire
Effects on Grasses and Forbs
4.Fire
Effects on Tree and Shrubs
5.Fire
Effects on Livestock and Wildlife
6.Post-fire
Livestock Management
For further
information contact:
Darren Bruhjell
Phone: 250 371-6058
Email:
Darren.Bruhjell@gov.bc.ca
Greg Tegart
Phone: 250 260-3035
Email: Greg.Tegart@gov.bc.ca
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