INTRODUCTION
Much of the vegetation of KwaZulu-Natal is maintained as
grassland by regular burning. Most grasslands would become dominated by scrub
thickets or forest if fire were excluded from the system. Lightning and rock
falls are thought to have been the major cause of fires before the arrival of
mankind, and these sources still start many fires in, for example, the KwaZulu-Natal
Drakensberg each year. The early inhabitants of KwaZulu-Natal used fire as an
aid to hunting and to encourage the growth of geophytes (plants with bulbs and
tubers which were used as food). With the advent of pastoralism, fire was used
particularly in the sourveld areas to improve the quality of veld grazing.
Grass burns most readily when dry. In KwaZulu-Natal, the
grasses generally become dormant and dry towards the end of May or early June.
Regrowth normally starts in September. Fires caused by lightning would have
occurred mainly during August and September, whilst rockfalls may also have been
the cause of fires during the dry winter months. Early hunters are also likely
to have set fires at these times. The grassland vegetation of KwaZulu-Natal has
apparently evolved under a system of regular burning and is therefore well
adapted to regular burning when dormant.
PLANT ADAPTATIONS
Many grasses are well adapted to fire, and indeed, unless they
are regularly and completely defoliated, they become moribund and die. Briefly,
the basic unit of the grass plant, the tiller, develops through the growing
season, producing leaves and eventually an inflorescence. At the same time, new
tillers are initiated at the base of the plant. After one or two seasons of
growth, the main tiller dies off and the newly-initiated lateral tillers will
develop the following season. Light is required for tiller development to occur,
and therefore if the old, dead material is not removed, the growth of new
tillers during the next season will be retarded. If no defoliation occurs over a
few years, then the whole grass tuft smothers itself (i.e. becomes moribund) and
dies. Burning during the dormant season removes the dead plant parts. The newly
initiated tillers are protected from damage by fire as they lie within the base
of the plant and, in some species, are underground. Once soil moisture and
temperature conditions are suitable for growth in the spring, these tillers will
begin to grow.
The adaptations of grasses to complete defoliation (i.e. newly
initiated tillers remaining at or below ground level during the dormant season)
do not apply if they are burned during the growing season (October to May). In
this period the tillers of many species, for example Themeda triandra (Redgrass),
are elevated well above ground level and defoliation by burning will destroy the
new growth. If the practice of burning during the growing season is continued,
those grass species which do not have tillers below ground at this time of year
will die out. For these reasons the grass communities of KwaZulu-Natal are not
adapted to burning during the growing season (refer to Production Guideline 7.2
in this series for more details of growth patterns in grasses).
Many trees and shrubs commonly found in the drier grassland
areas (e.g. Bioresource Groups 13, 14, 16 and 18) are also adapted to fire.
Although they are susceptible to fire in the seedling and early growth stages,
they are not killed by fire once they have passed these initial stages of growth
and development (refer to Production Guidelines 7.3 and 7.6 in this series for
greater detail on the effect of fire on woody plants).
BURNING AS A MANAGEMENT TOOL
Introduction
Fire is a useful and indispensable aid to veld
management and must form an integral part of the veld management strategy
practiced on the farm. The most important considerations relating to burning
grassveld are why burn, when to burn, how often to burn, what management to
apply following a burn and how to burn.
Why burn?
The five major reasons commonly given for using fire
in grassveld are:
- to burn off unpalatable growth left over from previous
seasons;
- to control the encroachment of undesirable plants in the
veld;
- to protect the veld (and farm) from wildfires and
accidental fires;
- to stimulate growth during those months of the year when
there is little young forage available, and thus provide green feed when it
does not occur naturally; and
- to destroy parasites.
Of these the first three are considered valid reasons, while
other two constitute bad management practices. Each is discussed in more detail
below.
Burning to remove old, dead overburden of
grass
To remove all the grass that accumulates during a
season by grazing alone is difficult. In practice, unpalatable, low-quality
herbage accumulates during a grazing season, particularly on the less-acceptable
plants. This leads to an overall lower quality of forage on offer to the
animals, with the new season's growth being diluted with low-quality residual
herbage from past seasons. In addition, accumulated dead growth from the
previous season results in tillers within the tuft becoming smothered and as a
result they might die. There is no replacement of these tillers because basal
buds die with the parent tillers or are smothered by dead herbage. This moribund
herbage must therefore be removed by fire.
Research indicates that the new growth following a burn is
more nutritious than new growth in unburned veld (although the difference
disappears as the season progresses). Many farmers, therefore, tend to burn
annually (particularly sheep farmers) in order to provide animals with the
highly-nutritious herbage which accumulates after a burn, and to remove old
low-quality herbage left over from the previous growing season. The farmer must,
however, consider the negative effects of annual burning on forage production
from veld. This aspect is discussed in the section: "How often should the
veld be burnt?".
Burn to control invader species and bush
encroachment
Invasion by undesirable species occurs in both
under- and over-utilized veld. A weakening of the competitive ability of the
grass component permits an encroachment of invader species. Fire can assist by
destroying the seedlings of invader species and by increasing the competitive
ability of the grass sward. Conditions must, however, be favourable and it is
necessary to burn when conditions will ensure a hot fire (see below).
Fire may be used effectively to control at least some
encroaching plants. In sourveld areas where Leucosidea sericea (Ouhout)
and other similar shrubs and bushes begin to encroach on grassveld, fire can be
used, initially at two-year intervals and later at longer intervals (every four
years), to control the trees. The veld should be rested for a period prior to
the burn to ensure the accumulation of sufficient fuel loads. The timing of the
burn is also important, as a very hot fire is required to cause die-back of
shrubs and trees. (Note that fire alone will not kill the trees, it will merely
kill off top growth. Follow-up fires are required to keep the trees short and
limit their competitive effects on grass growth). Research indicates that the
conditions required for a fire to be sufficiently hot to cause die-back of trees
are: a fuel load (comprising mainly of grass) of more than three tons of dry
matter per hectare; an air temperature above 25EC; a relative humidity of 30% or
less; and a head-fire (i.e. burn with the wind) must be applied.
The same approach should be used to control bush in the mixed
and sweet grassveld areas. It is true, nonetheless, that many shrubs and trees
coppice after burning. Here effective control of shrub and tree growth can be
achieved only if browsers can be introduced to use the coppice growth and
thereafter to reduce the tree's potential to recover after being burnt (refer to
Production Guideline 7.6 in this series for more information on the effect of
fire on woody plants).
Burning as a security measure
The development of a firebreak system is essential
in most areas if veld fires are to be safely contained. In fact, many farmers
burn their veld late (after the commencement of plant growth) merely for the
reason that "it was too dangerous to burn at the recommended times".
This is usually the result of an inadequate firebreak system. A well-planned
system of firebreaks is an invaluable aid in any veld burning programme. A few
internal breaks will ease the task of burning off selected areas of veld within
the farm boundaries. With such a system, veld burning may be carried out
efficiently, safely and effectively. Furthermore, firebreaks on farm boundaries
are required by law to protect adjacent properties from runaway fires.
Burning to stimulate out-of-season growth
The use of fire to produce out-of-season green
feed is practised by many farmers. The flush of green growth in early August
(after a July burn) or in April or May (after a March burn) is a very valuable
source of fodder when no other good-quality fodder reserves are available on the
farm. In the short term it does save the farmer the cost of buying or producing
feed for these times of the year. In the long term, however, out-of-season
burning does great damage to the veld. There is a loss of overall grass
production, a reduction in basal cover and therefore increased erosion, and a
change in species composition (the grass species which survive are not generally
those which are preferred by the grazing animal).
This was a widespread practice in earlier days when farmers
burned in June and July to provide early-season fodder particularly for sheep.
It is less prevalent now, mainly because of adequate fodder planning. New
growth does have a higher protein, TDN and mineral content compared to unburnt
grass in spring. This difference disappears during the season. Reduced
production does, however, limit intake of nutrients.
Early burning stimulates tufts to grow, drawing on reserves
held in the crown and root system of the plant for spring growth. This early
growth is grazed or frosted, causing an additional draw on stored reserves as
the plant regrows following grazing or frosting, seriously affecting the
vigour of the plant. Palatable species, in particular, are selectively grazed
and thus damaged.
A burn in the dry conditions which prevail during winter,
destroys surface mulch (organic matter). The mulch is responsible for
improving rain infiltration, retaining moisture and reducing erosion. This is
particularly so in humic soils. The loose organic herbage is, in addition,
washed away by early rains. Removal of the mulch thus reduces the effective
rainfall of the area.
After burning in June or July the soil surface is exposed
for a long period. Wind removes burnt herbage, surface mulch and soil. The
soil surface is compacted by the impact of raindrops in early spring storms
and then sun-baked, causing a crust. This situation results in high runoff and
reduced infiltration. The soil surface is also exposed to the sun and wind,
causing it to dry out. The dry profile results in an increase in species such
as Microchloa caffra. Contrary to popular opinion, firebreaks (which
are burnt in late autumn and early winter) do not produce ‘the best veld’.
(Note, as a point of interest, that the effects of early burning on soil
moisture can be clearly demonstrated by auguring in a firebreak and in the
adjacent veld. The firebreak - which is burned in May/June - will have a much
drier soil than the adjacent un-burnt veld).
Farmers often burn after the growing season has commenced
for a number of very practical reasons. For example the area may have just
gone through a drought and if the farmer burns his veld in early spring and
the ‘spring’ rains are late, he may have no roughage at all for the stock.
There may, therefore, appear to be quite rational reasons why the farmer will
delay burning until late in spring or early summer. However, once grass growth
has commenced, burning results in a very serious set-back to the grass plant.
Many of the new-season's tillers might be destroyed, necessitating the
development of an entirely new set of tillers. This delays growth
considerably. Close grazing thereafter results in further loss in vigour of
the plant. Also, stored reserves, used to initiate growth in spring are
depleted resulting in low vigour potential of the plant to regrow following a
late burn. Redgrass (Themeda triandra) is particularly susceptible to
late burning and will eventually die out in veld which is regularly burned
after spring growth has been initiated.
Late summer or autumn burning is practised, mainly by sheep
farmers, to fill a fodder flow gap for ewes and their lambs during autumn and
winter. Because autumn is the time when the plant stores the reserves which
are required to maintain it over winter and to have the energy to produce new
growth in spring, grazing of out-of-season growth in the autumn prevents these
essential survival processes from occurring. The vigour of the plant is thus
drastically reduced as is the livestock production potential of the veld.
Out-of-season burning cannot be justified on economic or
biological grounds. This is because of the reduction in forage production
potential, the deterioration in veld condition, plant vigour and basal cover,
and the soil loss which follows such a practice.
Burning to control parasites
Parasites, such as ticks, are not effectively
controlled by fire. For example, to escape fire, ticks fall to the ground and
enter cracks in the soil. Most fires do not influence soil temperatures and the
ticks are not harmed. The use of fire therefore cannot be justified for this
purpose. Dipping remains the only effective measure to control ticks.
When to burn?
Ideally, veld should be burned at a time which will
ensure that the leaf canopy will recover in the shortest possible time after the
burn. Research has shown that this ‘ideal’ time is in early spring just
after first good ‘spring rains’ (15 mm within 24 hours). At this time soil
temperatures have started to rise and moisture becomes available for plant
growth. In most areas (except on moist sites, such as wetlands), veld which is
burned too early remains bare until after the first good rains. Such early
baring of the soil, while it may have no appreciable short-term effect on plant
recovery when the spring rains arrive, may be expected to have an adverse
long-term effect, as the chances of erosion by both wind and water are
increased. In addition, veld which is burned early (June or July) does not
recover to a stage acceptable for grazing any earlier than veld which is burned
in August or early September.
In practice it is difficult to identify the ‘ideal’
burning time, especially if the first effective spring rains are preceded by
smaller rainfall events which, together with increasing temperatures, cause some
plant growth. Hence, when the first effective rains do fall the grass may
already be growing. The farmer also needs to plan in advance, and it is often
impossible to base the timing of his programme on an unpredictable event such as
the ‘first spring rains’.
The following points may be used as a guide and form the basis
of the Veld Burning Guidelines for KwaZulu-Natal.
Burning veld at a stage when the leaf canopy will recover as
rapidly as possible will ensure the greatest raindrop interception, retention
of moisture and therefore rapid growth. The earliest date after which burning
should be considered is therefore based on long-term climatic records which
are used to indicate when the temperatures rise and spring rains are most
likely to occur. These criteria have been used to determine the earliest date
for burning for each Bioresource Group in KwaZulu-Natal.
Growth in veld where the area is inherently moist (i.e.
moisture in not limiting to plant growth) is generally initiated by increasing
temperatures. In such areas it is often necessary to burn before the first
spring rains have fallen. A ‘last date’ for burning is therefore suggested
for all Bioresource Groups. This is done to limit the negative effects of late
burning (see above). It is always advisable to burn as soon as possible after
the first date given in the Veld Burning Guidelines for KwaZulu-Natal.
Veld rested the previous season, or latter half of the
previous season, builds up vigour and has an extended translocation period.
Stored reserves should therefore be high and spring growth is usually more
vigorous and initiates at an earlier date than in unrested veld. The blanket
of ungrazed herbage also stores more moisture in the soil profile. Veld which
has been rested for the whole of the previous season could therefore be burnt
earlier than veld which had not been rested.
- Burning in the dry Thornveld areas
Because the veld in these areas is sweetveld, grass should
remain acceptable to animals through the winter and ungrazed herbage can be
removed by the animal instead of by fire. Certain bushveld areas do, however,
tend to become moribund after a season of high rainfall. The excess, moribund
herbage can only be removed by burning. Also, burning can be used for bush
encroachment control purposes. (Note that the permission of the Executive
Officer of the Department of Agriculture is required before burning in
Bushveld areas - see the Veld Burning Guidelines for KwaZulu-Natal in
Production Guideline 2.8 for further information).
How often should veld be burned?
Ideally, one third to one quarter of the veld should
be rested each year. The remaining two thirds (or three quarters) should be
managed to achieve good utilization of the grass by the end of the grazing
season. The rested veld could be utilized with the aid of a suitable lick during
autumn and winter. Any herbage remaining in the rested area should then be
burned at the beginning of the following season, and a new area put up to rest.
This means that veld should be burned every three to four years. In practice,
this ‘ideal’ situation does not work because (1) there are usually
insufficient camps available per herd; (2) uniform utilization of the grass may
not be achieved; (3) above-average grass production during good seasons leads to
dry matter accumulation; and (4) animals will graze certain grass species only
at certain times of the season. Old, low-quality grass will always accumulate in
sourveld and mixed veld areas. The farmer must strive towards the ‘ideal’ by
subdividing existing camps and following a flexible rotational grazing system.
Where the problems outlined above occur, the following guidelines should be
used:
- never burn more than half of the veld on the farm each
year;
- do not burn more frequently than once every 2 years; and
- do not burn if less than one third of the total seasonal
production is left from the previous season.
As discussed earlier, some farmers tend to burn the veld
annually to provide their animals with the highly nutritious re-growth which
occurs after a burn. The problem with annual burning, though, is that it leads
to a drastic reduction in dry matter production. Burned veld is not as
productive as unburned veld, and by the end of summer burned veld would have
produced approximately one third less dry matter than unburned veld. For
example, if the production potential of the veld is 3 300 kg of dry
matter per hectare per annum, only 2 200 kg will be produced in the
season after the burn. Can the farmer afford to lose 1 100 kg of
potential feed per hectare each year?
What management should be applied after a burn?
Post-burning management is critical and should be
aimed at maintaining a vigorous, competitive sward. The most important effect of
grazing is the removal of the grass plant's ‘factory’ (its leaves). This ‘factory’
provides the plant with energy for growth. After a burn, therefore, the plant
must have sufficient time to produce leaves before grazing may commence.
Research has shown that repeated defoliation during the growing season reduces
potential grass production. It has also been shown that early defoliation
following a burn is related to the depression of dry matter production. Up to
60% of the total season's dry matter production could be lost as a result of
grazing too soon after a burn.
In terms of veld management, then, veld should not be grazed
too soon after a burn. A rule of thumb is that the grass plant may be grazed
when the first leaves have reached from 10 to 15 cm. At this stage there
should be sufficient leaf herbage left for the plant to continue growth after
the animal has taken a bite. If the veld has been burned just after good spring
rains (e.g. mid-August), it should be ready for grazing approximately eight
weeks after the burn (e.g mid-October). This period might be shorter or longer,
depending on how favourable conditions are for plant growth after the burn, and
on the vigour of the veld.
Resent research has, however, suggested that for good sheep
production the sheep must graze as soon after the burn as possible. To limit the
negative effects of this practice the veld must be rested for the whole of the
following growing season. The full season's rest should provide the plants with
sufficient vigour to recover from severe grazing by sheep in the previous
season.
How to burn
The burning method a farmer uses is critical to grass
production. If the crown of the plant is moist, very little damage is done to
the emerging tillers, resulting in rapid regrowth after a spring burn. A head
fire, that is burning with the wind, throws the heat upwards, removing topgrowth
without burning into the grown of the tuft. With the heat being distributed well
above the grass canopy a head fire is also effective for bush control purposes.
Head burns are therefore advised in almost all circumstances.
A back burn (burning against the wind)
subjects the ground surface and crown of grass tufts to excessive heat and thus
damage. Burning against the wind is therefore discouraged. Time of the day and
air temperature are also important. When burning to remove old, moribund grass,
the ideal conditions are considered to be when air temperatures are below 20EC
and the relative humidity is above 50%. These conditions are most likely to
occur before 11h00 and after 15h30.