Marloth Park Management Plan. - Nkomazi Local Municipality
Marloth Park Management Plan. - Nkomazi Local Municipality Marloth Park Management Plan. - Nkomazi Local Municipality
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
- Page 59 and 60: Table 6: Browsing capacities for th
- Page 61 and 62: INTRODUCTION ESTIMATION OF HERBACEO
- Page 63 and 64: The resulting Large Stock Units are
- Page 65 and 66: INTRODUCTION GAME MANAGEMENT ON MAR
- Page 67 and 68: STOCKING RATES Current stocking The
- Page 69 and 70: Table 10: The current stocking dens
- Page 71 and 72: Recommendations on stocking rates C
- Page 73 and 74: High selectivity grazers Blue wilde
- Page 75 and 76: Waterbuck Kobus ellipsiprymnus Ogil
- Page 77 and 78: Space requirements: Kudu have range
- Page 79 and 80: Recommendation: The range requireme
- Page 81 and 82: Food preference: Steenbok utilise A
- Page 83 and 84: Table 12: The potential stocking de
- Page 85 and 86: Table 14: The potential stocking de
- Page 87 and 88: Table 15: The recommended stocking
- Page 89 and 90: The proteins may be less available
- Page 91 and 92: When urea is incorporated into a ph
- Page 93 and 94: Recommended intake for game is 150
- Page 95 and 96: Ticks The main parasite of concern
- Page 97 and 98: Figure 12: Sketch of Cyphostemma /C
- Page 99 and 100: NOXIOUS AND INVASIVE WEEDS An invas
- Page 101 and 102: Management plans need to be reviewe
- Page 103 and 104: Ricinus communis, Solanum sisymbrii
- Page 105 and 106: Although soil treatment with chemic
- Page 107 and 108: Planning errors must be expected, a
- Page 109: To further reduce grazing pressure
- Page 113 and 114: TIME OF BURNING Least damage is cau
- Page 115 and 116: A low intensity fire will be achiev
- Page 117 and 118: Recommendations for Marloth Park Ma
- Page 119 and 120: Surface erosion will reduce water i
- Page 121 and 122: Several different types of waterhol
- Page 123 and 124: Stones Ground level Reinforced conc
- Page 125 and 126: For safety reasons these requiremen
- Page 127 and 128: Adaptive management Applying adapti
- Page 129 and 130: Figure 15: Location of the monitori
- Page 131 and 132: Appendix 1 (Continue) A list of tre
- Page 133 and 134: Appendix 2 (Continue) A list of gra
- Page 135 and 136: Appendix 3 (Continue) A list of for
- Page 137 and 138: Appendix 3 (Continue) A list of for
- Page 139 and 140: Appendix 4: Alien invaders found on
- Page 141 and 142: Appendix 5: Frequency occurrence of
- Page 143 and 144: Appendix 5: Frequency occurrence of
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- Page 155 and 156: Appendix 6: Photographs of each veg
- Page 157 and 158: Appendix 6: Photographs of each veg
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