Marloth Park Management Plan. - Nkomazi Local Municipality

Marloth Park Management Plan. - Nkomazi Local Municipality Marloth Park Management Plan. - Nkomazi Local Municipality

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The following seed mixture is recommended 11 : • Guinea grass Panicum maximum • Blue buffalo grass Cenchrus ciliaris • Finger grass Digitaria eriantha • Weeping love grass Eragrostis curvula • Lehmann’s love grass Eragrostis lehmanniana • Large-seed bristle grass Setaria incrassata Additional veld recovery can be achieved by supplementing the animals using a grass seed enriched lick. Grass seeds ingested while utilising the lick is passed through the digestive tract and deposited in the veld where germination can take place. Although the immediate effect is not noticeable, the long-term benefits in increased forage production can be an advantageous to Marloth Park. Another method of rehabilitation and habitat improvement is where a seed mixture is imbedded in a cow dung patty, approximately 10cm x 10 cm x 3 cm in size, and then distributed throughout the veld. These patties can be made and sold to property owners, who wish to participate in managing Marloth Park, to recover the cost. FIRE REGIME Before the advent of white man, game consisting of both grazers and browsers occupied vast areas of Africa. Game animals tended to graze veld areas fairly short and then moved on. Natural resting was thus implemented at different seasons and this allowed for vigorous grass growth. Grass reserves built up towards the end of the growing seasons and this allowed for lightning induced fires every few years. The grass reserves were adequate to create hot fires, which damaged woody seedlings, thus increasing grass competition. Fires were therefore, responsible for keeping the veld from being dominated by trees. The fire climax grasslands (sour grassveld) and savanna areas of the world owe their existence to fire, which has for long been part of their development. Fire is therefore, to be accepted as an inherent requirement of vegetation in maintaining an ecological balance. If fire is as a factor is to be removed form the system it can be expected that some changes in vegetation will occur. The implementation of a natural fire regime would therefore be ideal. Human interference has, however, made this almost impossible to obtain. On most ranches and conservation areas constant grazing pressure, despite rotational resting practices, and lightning induced fires play a significant role in regulating successional development of the vegetation. 11 Agricol (Pty) Ltd. P O Box 300, Brackenfell, 7560. Tel: (021) 981 1126 © Ecological Associates/ Marloth Park 103

Lightning induced fires can also cause a substantial loss of grazing land if adequate firebreaks are not in place. However, the simulation of a natural fire regime should be attempted to compensate for the absence of natural fires. The following are the objectives for using fire in veld management: Removal of old, unpalatable and unacceptable growth from the previous season, which can smother new growth. To destroy parasites such as ticks. Control of undesirable woody or herbaceous invaders that reduce the production of the grass layer. Areas can be burnt to induce rotational grazing. Firebreaks can be made to protect the veld. Another reason quoted for burning veld is to stimulate an out-of-season “green-pick”. This is often done during the summer, late autumn or late winter to provide green forage for grazing animals. Burning at these times is harmful because it: Reduces the vigour of the grass sward Reduces the canopy and basal cover of the grass sward Increases the run-off rainwater Results in increased soil erosion Adequate removal of top-growth by grazing alone is difficult in sourveld areas, although it may be achieved in intensive grazing systems. In sourveld areas, unpalatable low quality material accumulates on the less acceptable plants in particular, and burning must be resorted to remove this material if the plants are not to become moribund and die. Veld will deteriorate if it remains unutilised for any length of time. Therefore, where grass growth is rapid, and where there is no alternative method of utilizing the top growth (such as by grazing or mowing), frequent burning is advisable. Although fire can be used to control ticks, this is considered ineffective and generally not recommended. Fire is considered as a natural phenomenon in regulating bush encroachment and maintaining grasslands. The effectiveness of fire for the control of bush encroachment is, however, doubtful. Fire is generally more effective in controlling bush encroachment in the initial growth stages, but become less effective as the trees grow above the grass layer. © Ecological Associates/ Marloth Park 104

Lightning induced fires can also cause a substantial loss of grazing land if adequate firebreaks<br />

are not in place. However, the simulation of a natural fire regime should be attempted to<br />

compensate for the absence of natural fires.<br />

The following are the objectives for using fire in veld management:<br />

Removal of old, unpalatable and unacceptable growth from the previous season, which<br />

can smother new growth.<br />

To destroy parasites such as ticks.<br />

Control of undesirable woody or herbaceous invaders that reduce the production of the<br />

grass layer.<br />

Areas can be burnt to induce rotational grazing.<br />

Firebreaks can be made to protect the veld.<br />

Another reason quoted for burning veld is to stimulate an out-of-season “green-pick”. This is<br />

often done during the summer, late autumn or late winter to provide green forage for grazing<br />

animals. Burning at these times is harmful because it:<br />

Reduces the vigour of the grass sward<br />

Reduces the canopy and basal cover of the grass sward<br />

Increases the run-off rainwater<br />

Results in increased soil erosion<br />

Adequate removal of top-growth by grazing alone is difficult in sourveld areas, although it<br />

may be achieved in intensive grazing systems. In sourveld areas, unpalatable low quality<br />

material accumulates on the less acceptable plants in particular, and burning must be resorted<br />

to remove this material if the plants are not to become moribund and die. Veld will deteriorate<br />

if it remains unutilised for any length of time. Therefore, where grass growth is rapid, and<br />

where there is no alternative method of utilizing the top growth (such as by grazing or<br />

mowing), frequent burning is advisable.<br />

Although fire can be used to control ticks, this is considered ineffective and generally not<br />

recommended. Fire is considered as a natural phenomenon in regulating bush encroachment<br />

and maintaining grasslands. The effectiveness of fire for the control of bush encroachment is,<br />

however, doubtful. Fire is generally more effective in controlling bush encroachment in the<br />

initial growth stages, but become less effective as the trees grow above the grass layer.<br />

© Ecological Associates/ <strong>Marloth</strong> <strong>Park</strong> 104

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