
agricultural production guidelines
veld in kwazulu-natal
Veld in KwaZulu-Natal
| Co-ordinated
Extension |
KwaZulu-Natal
Veld 7.4 1999 |
GRASS AND BUSH
C R Hurt
ARC - Range and Forage Institute, Cedara
Grass Dynamics
Bush Dynamics
INTRODUCTION
The savanna regions of KwaZulu-Natal form an important part of
extensive beef and game ranching systems in the province. Correct management of
the vegetation is therefore essential in order to ensure the long-term
productivity of these areas. Much of the savanna in KwaZulu-Natal can be
classified as sweetveld (i.e. the herbaceous layer retains its acceptability and
nutritive value after the grass plants have reached maturity). Savanna
ecosystems are extremely resilient, and are able to recover rapidly following
stress periods (e.g. drought, heavy grazing), provided that a major loss of
top-soil has not occurred. Savanna functioning is dependent, to a large extent,
on a balance which exists between the bush component and the herbaceous layer,
and, depending on objectives, management is able to shift the balance in favour
of either the bush or grass component. In the savanna areas of KwaZulu-Natal,
where cattle and game ranching enterprises are common, it is essential that a
healthy grass cover is maintained between trees and shrubs. If poor grass cover
exists, animal production declines rapidly. Poor grass cover results from
overgrazing, which, in turn, encourages the woody plants to increase in density
and become more competitive, thereby causing an even greater decline in the
grass production. In this Production Guideline the balance and interactions
between grass and woody plants are examined, and a theory is provided for the
management of the vegetation in order maximise animal production. Many of the
concepts described in Production Guidelines 7.2, 7.3, 7.5, 7.6 and 7.7 in this
series have relevance to the bush/grass balance, and should therefore be
referred to.
GRASS DYNAMICS
Why does grass production decrease?
Overgrazing or continual heavy stocking causes
particularly the palatable grass plants to lose vigour as a result of the
repeated removal of leaves (the plant's ‘energy factory’) and the constant
drain on its nutrient reserves. When the plant is not able to replenish these
reserves by producing new leaves during rest periods to carry out
photosynthesis, it will eventually die, and its place will be taken by other
grasses which are either better adapted to heavy grazing, or which are
relatively less palatable.
As the desirable plants become weaker and die off, the number
of roots present in the upper layers of soil decreases and this reduces the
competitive ability of the grasses. Bare areas between grass plants also become
larger as the grasses become smaller or die. This causes a decline in the
effective rainfall in the area as a result of increased runoff, and gives rise
to a situation usually blamed on ‘droughts’. These conditions are ideal for
woody plants to establish themselves, and eventually take over areas where grass
previously predominated.
How does grass keep the bush in check?
Grasses and mature woody plants use different areas in
the soil profile to obtain moisture and nutrients. Grass roots are mainly found
in the upper soil layers, while woody plants are able to extend their roots to
utilize moisture and nutrients at deeper levels, as well as in the topsoil. It
is easy to see that once a woody plant has extended its roots to the deeper
horizons (i.e. once they have become established), the grass roots will not
compete with them for water and nutrients.
However, when the seed of a woody plant germinates, it has to
compete with the grasses for moisture and nutrients in the upper soil layers
until it can extend its roots to soil layers below those utilized by the
grasses. At this stage the seedling is most vulnerable, since the root system of
the grass plant is more extensive than that of the woody seedling. If the grass
layer is in a healthy, vigorous condition, a mass of roots will be present, and
will offer strong competition to the young woody plant. A period of stress (e.g.
mid-summer drought) will therefore often result in the woody seedling dying. If
a healthy, competitive grass layer is maintained, it will only be during periods
of above-average rainfall that the woody plants are able to establish
themselves.
On the other hand, if the grass layer is in a poor condition
due to overgrazing, or because it has become moribund as a result of infrequent
burning, relatively fewer roots will be present and will therefore offer less
competition to the woody seedling. Seedlings will stand a greater chance of
surviving any stress period and will be able to establish their root systems in
the subsoil layers. Once this takes place, the woody plant is unlikely to die as
a result of competition from other plants.
BUSH DYNAMICS
Why does the bush thicken up?
Once woody plants become established in areas that
were previously grassland or open savanna, the grasses are placed at a
disadvantage due to competition from the woody plants (i.e. for moisture,
nutrients and light). This is due to the fact that the roots of the woody
plants are present in both the upper and lower soil layers. This increased
competition results in a further decline in grass production, and promotes the
creation of better conditions for the establishment of seedlings of woody
plants. Eventually a situation is reached where the woody species start to
compete with one another for moisture, nutrients and light, and their growth
becomes retarded. This is the case where a short, dense shrub layer with a
closed canopy virtually prevents the growth of any grass plants. Such
situations are now common over a large part of the KwaZulu-Natal savanna
areas, and can be ascribed primarily to poor veld management practices and old
land situations.
Can trees control trees?
The density of woody individuals which develops
depends on the potential of a piece of land to provide the resources needed for
growth (moisture and nutrients). This potential is called the carrying capacity.
Once the density of woody species reaches the carrying capacity of the land,
individuals will also start competing with one another for moisture, nutrients
and light. At this stage, growth is reduced considerably and the trees do not
exceed a certain height, depending on the species and the number of individuals
of each species present. Virtually all the energy which is produced by metabolic
processes in the plant is used for maintenance, but minor fluctuations will
occur in sympathy with the erratic nature of the rainfall. It is only on the
death of an individual that its resources, which were previously unavailable to
other plants, become available. The individuals in its immediate vicinity will
then be able to continue growing until the carrying capacity is once again
reached.
To illustrate this concept, consider the
following example. The carrying capacity of one hectare of land dictates that it
is able to support, for example, 2 000 sweet thorn trees 1 m high, or 1 000
sweet thorn trees of 1.5 m, or 500 trees of 2.5 m, or 200 trees 3.5 m high.
Various intergrades are possible, but in general, there is a distinct
relationship between the size of the individuals and the number of individuals
present. Obviously, as the trees increase in density, the spaces between them
decrease. Conversely, as the trees grow larger, their root systems and canopies
extend over a larger area and the spaces between individuals become greater.
They therefore make a greater demand on the resources of the area, and thus the
larger the individuals are, the fewer individuals will be supported by the
available resources.
Thus, once a situation is reached where the
carrying capacity of the land has been attained, existing trees will outcompete
or suppress the growth of younger woody plants that germinate between them. On
the other hand, when a tree dies of natural causes, other woody plants will be
able to take its place. Although little research has been conducted on this
theory in KwaZulu-Natal, it has potential as a long-term means of keeping areas
open and productive. The concept here is rather to maintain a low density of
large, widely-spaced trees, than to encourage a high density of smaller
individuals by repeatedly removing all, or most of, the smaller trees.
Widely-spaced trees will favour grass growth and access by animals.
In conclusion, it can be seen that it is
critical that the vitality of the grass sward be maintained in order to keep a
competitive balance between the woody and herbaceous components of savanna
vegetation.
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