INTRODUCTION
Approximately 5 059 700 ha of veld is used for extensive
grazing in KwaZulu-Natal. Of this area about 2 287 500 ha is occupied by small
scale farmers and is utilized mainly on a communal basis.
Much of the Province’s grazing land is in poor to moderate
condition, particularly in the communal areas where it is difficult to implement
a veld management system. This situation leads to unsatisfactory veld production
and accelerated loss of water and soil (see Production Guideline 7.1 for more
detail on soil erosion in veld). For example in the Tugela River catchment which
consists mainly of veld, the sediment lost is equivalent to 5.2 tons per ha per
annum. A part of this loss could be attributed to veld in poor condition as a
result of over-grazing. The rate of soil formation however is less than 1 ton
per ha per annum resulting in a nett loss of soil.
Stocking rate has the greatest impact on veld condition and
animal performance. On farms where commercial livestock production systems are
followed the average stocking rate on veld is 3.5 ha per AU which is well within
the recommended norms. In the communal grazing areas there are 1 272 700 AU on 2 287 500 ha of land which translates to a very heavy stocking
rate of 1.8 ha/AU. Studies have shown that such stocking rates would inevitably
lead to a deterioration in veld condition, particularly in areas which receive
low and erratic rainfall.
IMPORTANCE OF VELD CONDITION
Veld condition reflects the vigour and productivity of veld,
relationships which have been well illustrated in studies at the Free State
University where veld was monitored over 15 years to measure differences among
sites with different veld conditions. The average rainfall over the period was
520 mm. The results of the study are given in Table 1.
It is obvious that the production from the poor veld is not
only 3.5 times less than veld in good condition, but the erosion is 6.5 times
more and the runoff twice as much. With steeper slopes and higher rainfall the
results could be more significant.
Table 1. The effect of veld condition on runoff, soil loss,
water use efficiency (WUE) and dry matter production off veld in a 500 to 550 mm
per annum rainfall area.
|
|
Veld condition |
|
Good |
Moderate |
Poor |
|
Veld condition score % |
96.7 |
69.0 |
31.3 |
|
Basal cover % |
9.0 |
6.0 |
3.0 |
|
Runoff on a 4% slope |
4.8% |
6.8% |
10.2% |
|
Soil loss per ha (tons) |
0.6 |
1.4 |
3.9 |
|
WUE (kg DM per mm rain / ha) |
2.1 |
1.2 |
0.6 |
|
Grass production (kg DM / ha) |
1 022 |
598 |
281 |
HOW TO IMPROVE VELD PRODUCTION IN COMMUNAL
AREAS
An understanding of veld management principles is required to
ensure acceptable livestock production whilst maintaining the productivity of
veld (see Production Guidelines 1.1, 2.1, 2.2 and 2.3 of this series for more
detail on veld management principles). It must be stressed that there are no
fixed recipes. Specific areas of a grazing system must be treated as separate
entities each with their own potential for animal production. However, in the
communal areas it is often not practical or possible to implement a veld
management system which applies all of the principles. Thus the veld management
principles need to be discussed in the communal area context.
Separate veld types
Areas with different palatability and grazing
potential should be demarcated. This will depend on aspect, slope, soil type
and rainfall. The most effective means of separating veld types is fencing.
However, in the communal areas, features such as streams, ridges, mountains
and realigned roads could be used. The area boundaries could also be marked,
for example, with white stones. Where fences do not exist herders should be
employed to implement an appropriate grazing and resting system.
Grazing capacity
Stocking within the grazing capacity of the veld is an
important grazing principle because this directly dictates the calving or
lambing percentage, weaning mass and percentage off-take of animal products. An
‘economic’ stocking rate would optimise production but in the communal areas
an ‘ecological’ stocking rate occurs because numbers of animals are more
important than production for direct financial gain. It is therefore up to the
community to decide whether they wish to implement an ‘economic’ or an ‘ecological’
stocking rate. However, the inevitable consequence of implementing an ‘ecological’
stocking rate is a decline in veld condition and, ultimately, a reduction in the
potential of the veld for livestock production.
Resting of veld
Frequent intensive grazing reduces grass vigour and
yield. In order to maintain the vigour of the veld, it is essential to rest the
vegetation for the entire growing season at least once in 4 years.
In the communal areas the implementation of this principle
could have a marked beneficial effect on veld production. This would mean that
at least one quarter of the veld should be rested every year. In uniform veld
all that would be required is to divide the area into four equal areas. Where a
number of veld type units (VTU’s - see Production Guideline 2.2 of this series
for the detail of VTU’s) are involved, each demarcated area should, as far as
possible, have the same grazing capacity and VTU’s represented. The rested
veld would be an invaluable source of fodder during the winter.
Prevent top layer accumulation
Due to selective grazing, unpalatable residual herbage
accumulates and becomes moribund. This applies particularly to sourveld after a
period of rest where the veld should be burnt. However, in the communal areas
this should only constitute a problem where an ‘economic’ stocking rate is
implemented.
Bush encroachment
In the savanna areas, where bush is either encroaching
or thickening up grass production is detrimentally affected due to competition
from the trees. Preventive measures such as providing a hot burn or chemical
control are seldom necessary in the communal areas as chopping trees for
firewood and the browsing of goats are excellent control measures.
Livestock ratios
Veld grazed by sheep alone will invariably deteriorate
unless it is frequently rested. This is due to the selective grazing habit of
sheep. Veld will however be better utilised where cattle and sheep are run
together on the same area in a ratio of at least 1 AU of cattle to 1 AU of sheep
(6 sheep).
In the communal areas the grazing of cattle and sheep together
could be achieved. Also, because the number of cattle (on an AU basis) carried
on communal grazing lands exceeds that of sheep, the livestock ratio would be in
favour of cattle.
Stocking intensity
In situations where it is possible to operate a
multicamp system and, in particular, where it is difficult to demarcate areas
with the same size or grazing capacity, it is necessary to ensure that the
stocking intensity for all camps/grazing areas is similar. The stocking
intensity is expressed in grazing days per ha (GDH).
To achieve this the period of stay for each grazing area must
be established. The grazing period or period of stay is obtained by multiplying
the carrying capacity of the grazing area by the grazing cycle and dividing this
by the carrying capacity of the total area allocated for grazing (excluding the
rested area). An example, based on a four-camp/grazing area system, is given in
Table 2.