
agricultural production guidelines
veld in kwazulu-natal
Veld in KwaZulu-Natal
| Co-ordinated
Extension |
KwaZulu-Natal
Veld 2.5 1999 |
DETERMINATION OF GRAZING AND
BROWSING CAPACITY
J M B Smith
KwaZulu-Natal Department of Agriculture
M B Hardy
Western Cape Department of Agriculture
Importance of Stocking
Rate
Grazing Capacity and
Mean Annual Rainfall
Calculation of Browsing Capacity
INTRODUCTION
The development of a successful grazing management system for
a farm is largely dependent on the number of animals that a certain area of veld
is able to support. This concept of productivity of land is called the grazing
capacity of the veld and is the most important principle of grazing management.
It is dependent on a number of factors such as rainfall, veld condition, slope,
aspect and soil, among others. It is obvious, therefore, that the grazing
capacity of veld will vary considerably from area to area, hence the need to
fence off the different Veld Type Units (VTU’s) on the farm. It is important
that the grazing capacity of each of these VTU’s is determined individually.
IMPORTANCE OF STOCKING RATE
There are numerous examples of the effect of stocking rate on
production of animals. At Soutpan research station it was demonstrated that by
reducing stock a greater mass of weaners were produced on the same piece of land
(Table 1).
Table 1. Effect of stocking rate on weaner production
|
Stocking rate (ha/cow)
Number of cows
Calving percentage
Weaning mass (kg)
Total weaning mass (kg/ha) |
2.7
33
56
145
2 680 |
4.7
18
88
186
2 946 |
As the stocking rate is increased, animal performance in the
form of mass gain and calving percentage will decrease. Expressing this
performance in gain per ha will result in an increase up to a maximum, followed
by a decline. The maximum gain
per ha will occur when animal performance has already
decreased significantly. When considering profit this will be maximised where
performance per animal has declined by about ten percent of maximum gain per
animal. Therefore the optimum stocking rate should be close to that which
maximises individual animal performance.
GRAZING CAPACITY AND MEAN ANNUAL RAINFALL
Herbage yield
The grazing capacity of an area of land depends on
how much useful herbage (forage) is produced on that area. In general, there
is a positive correlation between veld herbage yield and rainfall during the
growing season. This correlation has been shown in the production of various
crops (e.g. the production of one ton of maize grain requires 100 mm of rain,
as does the production of 9 ton of sugarcane). The relation between grass
yield and rainfall was studied in thornveld at Matopos Research Station in
Zimbabwe. These results indicated that one millimetre of annual rainfall
produced approximately 3 kg of grass on a dry matter basis. A similar trial in
the Orange Free State examined grass yields in response to rainfall across
veld in different condition. The results of this study are presented in Table
2.
Table 2. Dry matter (DM) production of veld in different
stages of succession in response to rainfall (mm) in the central Orange Free
State. Mean annual rainfall was 712 mm
|
Veld conditions |
Good/Excellent |
Reasonable |
Poor/Critical |
|
Basal cover
Runoff
DM kg/ha
kg DM/mm rain |
9%
6%
2 256
3.2 |
6%
10%
1630
2.3 |
3%
20%
889
1.2 |
The above trial indicated that, with a deterioration in veld
condition and a decrease in basal cover, runoff of rainfall increases. This
reduces the effective rainfall and thus the herbage yield.
To determine the yield of grass, it is necessary to use the
rainfall which falls during the growing season (October to March) which, in
KwaZulu-Natal, is about 80% of the mean annual rainfall. This figure decreases
towards the coast and is 60% at Richards Bay.
The relation between rainfall, veld condition and grass
yield is presented in Table 3.
Table 3. General relations between veld condition and grass
dry matter (DM) yield and rainfall.
|
Veld condition |
Yield factor(grass yield, kg DM per mm
rain October - March) |
|
Excellent - 100%
Good - 80%
Average - 60%
Poor - 40%
Critical - <20% |
1 5
4
3
2
1 |
1 In the Sour Sandveld, use
one unit less for each veld condition class, i.e. 4, 3, 2 and 1.
The veld condition should be determined from the
composition, palatability and vigour of the species (see Production Guideline
2.4 of this series).
Stocking rate
The determination of grazing capacity provides the
farmer with a guideline of the stocking rate which should be applied to each
VTU on the farm. It is necessary to express stocking rate calculations in
terms of Animal Units (AU). An AU refers to an animal with a mass of 450 kg
which consumes 10 kg dry matter (DM) per day (i.e. about 3500 kg DM per
annum). The palatability and quality of the grass sward declines at different
rates during the late summer months according to the veld type. Herbage
consumption will therefore also vary. The estimated annual herbage consumed
per hectare for each veld type, excluding supplements, is presented in Table
4.
Table 4. Herbage consumption by livestock for different veld
types.
|
Veld type |
Bioresource Group |
Herbage consumption
(kg/AU/annum)
|
|
Sourveld
Sour/mixedveld
Mixedveld
Sweetveld |
3 to 11 & 15
1, 2, 12, 14 & 17
13, 16 & 18 to 20
21,22,23 |
2 500
2 750
3 000
3 500 |
One of the fundamental principles of veld management is to
limit the utilization of herbage to half of the total production. The axiom
"take half, leave half" is applicable in this regard. To determine
the stocking rate, the herbage yield should be assessed by multiplying the
average growing season rainfall (in mm) by the yield factor (Table 3). The
resultant yield per hectare is halved, and then divided into the annual
herbage consumption per AU to obtain the number of hectares required per AU.
In a sourveld area, for example, where the mean annual
rainfall is 800 mm, the growing season rainfall would be 640 mm (80% of 800
mm). With veld condition at 80% of the benchmark, the herbage yield would be 2
560 kg DM per annum per ha (640 mm x 4 kg/mm/ha - Table 3). Only half of the
yield should be utilized (i.e.
1 280 kg/ha). To determine the number of hectares required
per AU, divide 1 280 kg/ha into 2 500 kg/AU (Table 4). This gives a stocking
rate of 1.9 ha/AU.
In a mixed veld area, where the annual rainfall is 700 mm,
the growing season rainfall would be 560 mm (80% of 700 mm). With a veld
condition at 70% of the benchmark, the herbage yield would be 1 960 kg DM per
annum per ha. (560 mm x 3.5 kg/mm/ha - Table 3). Only half of the yield should
be utilized (i.e. 980 kg/ha). To determine the number of hectares required per
AU, divide 980 kg/ha into 3 000 kg/AU (Table 4). This gives a stocking rate of
3.0 ha/AU.
In the sweetveld, where Acacia trees have encroached
or thickened up, their effect on grass yield should be taken into
consideration when determining grazing capacities. This effect is measured in
terms of tree equivalents (TE). As the number of TE increase above 900 per
hectare, grass production declines. Tree equivalents are calculated from the
information collected when surveying the woody component of each VTU (see
procedure in Production Guideline 2.4 of this series). Since all woody plants
affect grass production, the number of tree equivalents is calculated by
adding the heights of all woody species sampled and dividing by 1.5. Thus one
tree, 3 m tall, is two tree equivalents, having twice the competitive effect
on grass production as a tree 1.5 m tall. A mean for the camp can be
calculated (as for the browse units) and converted to a per hectare figure.
This is then used to calculate the reduction in grazing capacity. The effects
of tree density on grass production is reflected in Table 5.
Table 5. Effect of tree density on grass production.
|
Tree density
(tree equivalent/ha) |
Portion of grass yield in relation to the
absence of trees (%) |
|
<900
900
1 200
1 500
1 800
2 100 |
100
90
85
70
50
30 |
In a sweetveld area with Acacia trees, where the
annual rainfall is 600 mm, the growing season rainfall would be 480 mm (80% of
600 mm).
With a veld condition at 70% of the benchmark, the grass
yield (where the TE per hectare is <900) would be 1 680 kg per ha (480 mm x
3.5 kg/mm/ha - Table 3). With 1 200 TE per ha the grass yield would be reduced
to 1 428 kg per ha (85% of 1 680 kg - Table 5). Only half of this yield should
be utilized (i.e. 714 kg/ha). To determine the number of hectares required per
AU divide 714 kg into 3500 kg/AU (Table 4). This gives a stocking rate of 4.9
ha/AU.
If browsers, e.g. goats, are to be used in the same area
they would be stocked according to the amount of browse available to them.
However, even under circumstances in which adequate browse is available to the
goats, approximately 20% of their intake is grass, so the grazer stocking rate
must be reduced even further to allow for this consumption by goats. In
addition, in areas where the A. karroo plants lose their leaves in
winter, goats (or other browsers) must subsist entirely on the grass component
during this period. Therefore, for example, it has been shown that for an area
where A. karroo has no leaves for 3 months of the year, the grazer
stocking rate must be reduced by 40% of the browser stocking rate
to allow for grass eaten by browsers.
CALCULATION OF BROWSING CAPACITY
If goats are to be run as browsers and to eat the minimum of
grass, the stocking rate of browsers (goats) should be based on the quantity of
available browse material produced by the palatable woody plants in each camp or
proposed camp. The browsing capacity of the trees and shrubs will depend on the
quantity of browse that is produced in the 1.5m-high browsing zone, since
anything higher is essentially out of goats’ reach.
Preliminary research in the Eastern Cape has shown that the
following numbers of palatable plants 1.5 m in size are needed for each mature
goat per year (Table 6).
Table 6. The number of browse units required per mature goat
in the different areas of the eastern Cape according to soil depth.
|
Catenal position |
Soil depth
(mm) |
Rainfall (mm) |
|
|
|
600 - 800 |
450 - 600 |
|
Crest
Midslope
Footslope/valley bottom |
200 - 500
500 - 1 200
>1 200 |
2 000
1 500
1 000 |
2 500
2 000
1 500 |
The number of plants in the camp must first be sampled (see
Production Guideline 2.4 of this series). Since the goats eat only palatable
plants, the number of palatable plants per hectare must be calculated.
Acceptability ratings are given for a range of species in Table 7. Note that
this information was obtained from studies conducted in the Eastern Cape
Thornveld. Farmers in the KwaZulu-Natal bushveld areas should consult with
experts or use their own experience to classify woody plants into the acceptable
and unacceptable categories.
Total BU/ha can be calculated for that camp using the method
given in Production Guideline 2.4 of this series, taking into account the
acceptability of the different species. By multiplying the number of BU per
hectare by the size of the camp the total BU for the camp will be calculated. To
calculate the browsing capacity for that camp divide the total BU for the camp
by the relevant number of BU/goat from Table 6. Each camp on the farm must be
similarly sampled to give the browsing capacity for the whole farm.
Table 7. The acceptability of various bush species to goats
in the thornveld areas of the Eastern Cape.
|
Acceptable |
Unacceptable |
|
Acacia caffra
Acacia karroo
Boscia oleoides
Capparis sepiaria
Carissa haematocarpa
Coddia rudis
Combretum caffrum
Cussonia spicata
Ehretia rigida
Euphorbia bothae
Euphorbia coerulescens
Grewia occidentalis
Grewia robusta
Olea africana
Pappea capensis
Phyllanthus verrucosus
Portulacaria afra
Rhigozum obovatum
Rhus lancea
Rhus lucida
Rhus macowanii
Schotia afra
Schotia brachypetala
Schotia latifolia
Scutia myrtina
Sideroxylon inerme
Tecomaria capensis
Ziziphus mucronata
|
Aloe ferox
Azima tetracantha
Brachylaena elliptica
Brachylaena ilcifolia
Diospyros lyciodes
Euclea undulata
Lippia javanica
Lycium Campanulatum
Maytenus heterophylla
Ozoroa mucronata
Plumbago auriculata
Protoasparagus setaceus
Ptaeroxylon obliquum
|
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