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 relative ecological index values are assigned: Decreasers - 10 Increasers Ia - 7 Increasers Ib - 7 Increasers IIa - 4 Increasers IIb - 4 Increasers IIc - 1 Invaders - 1 The maximum veld condition score of 1000 is based on 100 percent Decreaser grass species. The minimum veld condition score of 100 is based on 100 percent Increaser IIc or invader species. However, the occurrence of misses recorded can in effect reduce this value. According to the dominance of the various ecological groups the veld can be classify as in excellent condition if Decreasers dominate, in good to fair condition if Increaser Ia and Increaser Ib dominate, in fair to poor condition if Increaser IIa and Increaser IIb dominates, and in poor to very poor condition if Increaser IIc and invader grass species dominate. Veld in excellent condition is representative of a homogenous unit that is most productive in a specific area, and is considered most resilient if utilised with prudence. The veld condition score of a survey site in itself already gives an indication as to the potential of the veld, but is usually compared to the veld condition score of a benchmark site, determined using the same survey method. The benchmark value is taken as the potentially maximum value and divided into five equal portions (1 to 110 for very poor, 111 to 220 for poor, 221 to 330 for moderate, 331 to 440 for good and 441 to 550 for excellent condition) for evaluation. If no benchmark site is available for comparison, the following categories are implemented: Where a veld condition score of 0 to 39.9 % indicates veld in poor condition 40 to 60 % indicates veld in moderate condition 60.1 to 100 % indicates veld in good condition © Ecological Associates/ Marloth Park 39

Calculation of grazing capacity The combined veld condition and rainfall method, based on the following equation, is applied to calculate the grazing capacity in this study area. GC = -0.03 + (0.00289 * X1) + (X2 – 419.7) * 0.000633 Where: GC = grazing capacity in Large Stock Units (LSU) per hectare X1 = percentage veld condition score X2 = mean annual rainfall in mm per year. It is recommended that long-term rainfall data be used, as this will result in a grazing capacity value that is suitable for sustainable stocking rates. The use of short-term rainfall data, covering only 2 to 3 years, can result in unsustainable values due to the inability of a rancher to implement the required fluctuations in applying suitable stocking rates. As the veld condition and rainfall method was originally designed to calculate grazing capacities for cattle production, the values obtained from the equation should be tailored to fit the purposes of a wildlife ranch. Adjustment of the calculated grazing capacity value is necessary, due to the inability of the rancher to implement an effective rotational resting system, and to compensate for the selective feeding behaviour of wildlife. It is recommended that the calculated grazing capacity be reduced by 30 percent to facilitate these factors and ensure sustainable use of the natural resources without deterioration of the habitat. RESULTS AND DISCUSSION Veld condition All grass species are identified (Appendix 2) in the step-point field surveys on Marloth Park and the frequency of each grass species in every plant community calculated. A veld condition score and potential grazing capacity are calculated according to the relative frequency occurrence (Table 1) of the grass species in the various monitoring survey sites on Marloth Park. Plant community 1: The Chloris virgata – Acacia grandicornuta Low thicket This plant community is approximately 22 ha in size, and dominated by broad-leaved panicum Panicum deustum from the Decreaser category. The sub-dominant grass species is common carrot-seed grass Tragus berteronianus from the Increaser IIc (3) category. The veld condition score of 652 (Table 2) indicate that the veld is in good condition. © Ecological Associates/ Marloth Park 40

The following relative ecological index values are assigned:<br />

Decreasers - 10<br />

Increasers Ia - 7<br />

Increasers Ib - 7<br />

Increasers IIa - 4<br />

Increasers IIb - 4<br />

Increasers IIc - 1<br />

Invaders - 1<br />

The maximum veld condition score of 1000 is based on 100 percent Decreaser grass species.<br />

The minimum veld condition score of 100 is based on 100 percent Increaser IIc or invader<br />

species. However, the occurrence of misses recorded can in effect reduce this value.<br />

According to the dominance of the various ecological groups the veld can be classify as in<br />

excellent condition if Decreasers dominate, in good to fair condition if Increaser Ia and<br />

Increaser Ib dominate, in fair to poor condition if Increaser IIa and Increaser IIb dominates,<br />

and in poor to very poor condition if Increaser IIc and invader grass species dominate. Veld in<br />

excellent condition is representative of a homogenous unit that is most productive in a<br />

specific area, and is considered most resilient if utilised with prudence.<br />

The veld condition score of a survey site in itself already gives an indication as to the<br />

potential of the veld, but is usually compared to the veld condition score of a benchmark site,<br />

determined using the same survey method. The benchmark value is taken as the potentially<br />

maximum value and divided into five equal portions (1 to 110 for very poor, 111 to 220 for<br />

poor, 221 to 330 for moderate, 331 to 440 for good and 441 to 550 for excellent condition) for<br />

evaluation. If no benchmark site is available for comparison, the following categories are<br />

implemented:<br />

Where a veld condition score of<br />

0 to 39.9 % indicates veld in poor condition<br />

40 to 60 % indicates veld in moderate condition<br />

60.1 to 100 % indicates veld in good condition<br />

© Ecological Associates/ <strong>Marloth</strong> <strong>Park</strong> 39

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