Background Image
Previous Page  75 / 116 Next Page
Basic version Information
Show Menu
Previous Page 75 / 116 Next Page
Page Background

73

It should be noted that this model prediction is based on a typical farm in the North Western

Free State, where rainfall variability remains to be a key risk factor (i.e. lower yield assump-

tions for maize and soybeans). With the inclusion of pasture in a cash cropping system (as

in this particular example) at least 25% of the total area planted has a risk mitigating impact.

Management of pasture ley crops before the

successive grain cropping cycle

As part of the proposed pasture ley cropping system, no-till planting of the crop is essential

for reducing the risks of soil erosion. It is beneficial to plant directly into the plant residues,

which consist of pasture material from the ley cropping season/s that has been killed with

herbicide, one or two weeks before planting.

Intervals between the killing of the pasture ley crop and the planting of the successive crop

should be short, otherwise the residues, especially legume residues with their low C:N ra-

tio’s, will decompose very quickly. Grass ley pastures have the added advantage of taking up

N rapidly during the early rains, minimising the leaching loss and then releasing it to the crop

when killed by the herbicide.

Mixed grass and legume pastures are preferred from a grazing perspective compared to pure

monospecific grass pastures. Crops grown after pure grass ley pastures (especially grass

crops such as maize) could have yield restrictions due to an N-negative period and N-fertiliser

levels should be adjusted accordingly (around 30% higher).

To prevent the grass component of the mixed pasture ley crop to dominate, judicious cattle

grazing can be used to remove the larger grass canopy, which will benefit the legume com-

ponent. When grazing ley crops in the dry season (winter), it is essential to leave sufficient

well distributed plant cover on the soil surface for the successful re-establishment of either

the pasture or the successive grain crop.

This is a key compromise that has to be reached between the needs of the animals and of the

plants in the system.

Conclusions

Pastures are most likely to produce good profits compared to grain crops on a per hectare

basis, especially on soils that have accumulated effects of land degradation which will in-

creasingly limit the grain potential in future.

Secondly, pasture leys have significant benefits and improvements to ecosystems (especially

soil health), which are not always quantified to emphasise the dual purpose of the pasture

ley crop. However, the noticeable increases in grain yields after pasture ley crops will

provide some reflection on their additional rand value, other than just the revenue generated

from the pasture ley crop from cattle grazing.

Pasture ley crops improve the productivity and enhance the sustainability of mixed farming

enterprises. For such systems to be effective, it is imperative to conduct ongoing on-farm

research of these complex systems, especially to:

Understand the competition between crops and undersown legumes.

Determine the optimum sowing rates to maximise the subsequent benefit of the ley crop.

Study the seed dynamics of annual legumes.

Study the influence of herbicide residues associated with minimum/zero till cropping

systems, especially on legume pasture ley crop establishment and growth.

Develop management strategies which maintain the pasture ley species, while benefiting

the animal production component of the integrated CA system and not resulting in anti-

quality factors affecting the animal health.

Overall, the positive attributes of an integrated crop- and pasture-based livestock CA system

will facilitate the creation of a more sustainable grain production system.

For more information contact Dr Wayne Truter (

wayne.truter@up.ac.za )

, Mr Gerhard van der

Burgh (

gerhard@bfap.co.za )

, Dr Hendrik Smith (

hendrik.smith@grainsa.co.za )

or Mr Gerrie

Trytsman (

gtrytsman@arc.agric.za )

.

References

Jones, RK, Peake, DC, and McCown, RL. 1983.

The effect of various tropical legumes on nitrogen supply

. Annual

report 1982 - 1983, division of tropical crops and pastures, CSIRO: Australia. pp. 135 - 136.

Jones, RK, Dalgliesh, NP, Dimes, JP and McCown, RL. 1991.

Sustaining multiple production systems 4

.

Ley pastures in crop-livestock systems in the semi-arid tropics

. Tropical grasslands 25, 189 - 196.

Lloyd, Dl, Smith, KP, Clarkson, NM, Weston EJ and Johnson, B. 1991.

Sustaining multiple production systems 3.

Ley pastures in the subtropics

. Tropical grasslands 25, 181 - 188.

McCown, RL, Winter, WH, Andrew, MH, Jones, RK and Peake, DC. 1986.

A preliminary evaluation of legume ley

farming in the Australian semi-arid tropics.

In: Haque, I, Jutzi, S and Neate, PJH (Eds) Potentials of forage leg-

umes in farming systems of Sub-Saharan Africa. pp. 397 - 419. (ILCA: Addis Ababa.)

Wylie, P. 2007.

Economics of pastures versus grain or forage crops

. Tropical Grasslands 41, 229 - 233.