Marloth Park Management Plan. - Nkomazi Local Municipality
Marloth Park Management Plan. - Nkomazi Local Municipality Marloth Park Management Plan. - Nkomazi Local Municipality
• The aspect differs in its´ exposure to sunlight and therefore, in dryness. Areas with northern aspect are dryer than areas with southern aspect in the southern hemisphere. • The slope is mainly described as flat, average or steep. It differs in the amount of water runoff and proneness to erosion and therefore, in the availability of water and soil as a growth medium. The terrain form is documented as crest, mid-slope or valley which in this study. It influences the availability of water and the soil profile. • The geomorphology is described as flat, concave or convex, while the topography is described as mountain, ridge, plain, valley, pan or riverbank. Both influence the drainage of water. • The degree of trampling influences plant re-growth and proneness to erosion. • The degree of erosion influences the top layer of the soil and therefore, the availability of growth medium. • The drainage is recorded as wet or dry, as it influences the occurrence of plants that are adapted to these conditions. • The geology and rock cover influences the soil profile and soil type with soil being important as the growth medium. • The soil colour can indicate clay content and thus leaching of nutrients. • The clay content of the soil influences the availability of minerals and water to plants. • The canopy cover consists of the following groups: large trees, small trees, shrubs and forbs. Canopy cover influences suitable shaded habitat and therefore, the occurrence of specific plant species. • The biotic influences such as termites influence the habitat and the occurrence of plant species. The soil and its profile are of importance as they are the growth medium for the plants, supplying nutrients and physical support. © Ecological Associates/ Marloth Park 27
RESULTS AND DISCUSSION Analysis and synthesis of data collected on Marloth Park result in a classification of the vegetation. A total of 275 species were recorded. However, not all of the identified species were used in the classification of the plant communities. Those species, which occurred in low consistency, were omitted, as these species do not influence the interpretation of the data or the classification of the plant communities. A complete list of all tree (Appendix I), grass (Appendix 2) and forbs species (Appendix 3) encountered on Marloth Park has been compiled. The following plant communities were identified: The five major plant communities identified on Marloth Park (Figure 10) exhibit a close association with the study conducted of Lionspruit Game Reserve. However, two more plant community have been identified; the first is associated with the gabbro formation that traverses Marloth Park from east to west, and the second is based on historic utilisation. Fragmented variations also occur, but are relatively small and localised. Where these variations are considered of importance or warrant protection, they are discussed in more detail. The five plant communities on Marloth Park are: 1. The Chloris virgata – Acacia grandicornuta Low thicket 2. The Trichoneura grandiglumis – Combretum apiculatum Short bushland 3. The Themeda triandra – Acacia nigrescens Low bushland 4. The Spirostachys africana – Balanites maughamii Low bushland 5. The Dichrostachys cinerea – Tragus berteronianus Low bushland Plant community 1: The Chloris virgata – Acacia grandicornuta Low thicket This plant community consists of relatively small fragmented areas, characterised by the presence of deep sandy plains with well-leached soils. This leaching of soils is attributed to sub-surface, down hill, water-flow that transports minerals and clay particles to lower lying terrain forms. The most conspicuous tree species are red bushwillow Combretum apiculatum and velvet raisin Grewia flava. However, the presence of horned thorn Acacia grandicornuta, black monkey orange Strychnos madagascariensis and common hook thorn Acacia caffra is considered character species. Other tree species are marula Sclerocarya birrea subsp. africana, buffalo thorn Ziziphus mucronata, giant raisin Grewia hexamita, mallow raisin Grewia villosa, sandpaper raisin Grewia flavescens, silver cluster leaf Terminalia sericea, white-berry bush Flueggea virosa and velvet corkwood Commiphora mollis. © Ecological Associates/ Marloth Park 28
- Page 1 and 2: Ecological Associates Environmental
- Page 3 and 4: THE ASSESSMENT OF AVAILABLE BROWSE
- Page 5 and 6: LIST OF FIGURES Figure 1: Location
- Page 7 and 8: LIST OF APPENDICES Appendix 1: A li
- Page 9 and 10: Three different scenarios are analy
- Page 11 and 12: Ecosystems disturbed by clearing op
- Page 13 and 14: INTRODUCTION Although only a few ve
- Page 15 and 16: Figure 1: Location of the Marloth P
- Page 17 and 18: GEOMORPHOLOGY Looking down from the
- Page 19 and 20: Figure 4: Geology of the Marloth Pa
- Page 21 and 22: Tonalitic granite and gneiss A sect
- Page 23 and 24: Figure 6: Soil depth of the Marloth
- Page 25 and 26: Figure 7: Land Types of the Marloth
- Page 27 and 28: Figure 8: Land use in the Marloth P
- Page 29 and 30: A 610.1 B 104.0 C 7.4 D 19.9 E 39.8
- Page 31 and 32: INTRODUCTION VEGETATION CLASSIFICAT
- Page 33: METHOD For an initial and broad sca
- Page 37 and 38: The dominant grass species are broa
- Page 39 and 40: The characteristic tree species are
- Page 41 and 42: VELD CONDITION ASSESSMENT AND THE C
- Page 43 and 44: Degradation gradients are models th
- Page 45 and 46: The nearest grass species to each s
- Page 47 and 48: Calculation of grazing capacity The
- Page 49 and 50: Table 2: Contribution of ecological
- Page 51 and 52: Table 3: Grazing capacities for the
- Page 53 and 54: THE ASSESSMENT OF AVAILABLE BROWSE
- Page 55 and 56: X Y D1 Y Dimensional measurements:
- Page 57 and 58: RESULTS AND DISCUSSION The browsing
- 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
• The aspect differs in its´ exposure to sunlight and therefore, in dryness. Areas<br />
with northern aspect are dryer than areas with southern aspect in the southern<br />
hemisphere.<br />
• The slope is mainly described as flat, average or steep. It differs in the amount of<br />
water runoff and proneness to erosion and therefore, in the availability of water<br />
and soil as a growth medium.<br />
The terrain form is documented as crest, mid-slope or valley which in this study.<br />
It influences the availability of water and the soil profile.<br />
• The geomorphology is described as flat, concave or convex, while the topography<br />
is described as mountain, ridge, plain, valley, pan or riverbank. Both influence the<br />
drainage of water.<br />
• The degree of trampling influences plant re-growth and proneness to erosion.<br />
• The degree of erosion influences the top layer of the soil and therefore, the<br />
availability of growth medium.<br />
• The drainage is recorded as wet or dry, as it influences the occurrence of plants<br />
that are adapted to these conditions.<br />
• The geology and rock cover influences the soil profile and soil type with soil<br />
being important as the growth medium.<br />
• The soil colour can indicate clay content and thus leaching of nutrients.<br />
• The clay content of the soil influences the availability of minerals and water to<br />
plants.<br />
• The canopy cover consists of the following groups: large trees, small trees, shrubs<br />
and forbs. Canopy cover influences suitable shaded habitat and therefore, the<br />
occurrence of specific plant species.<br />
• The biotic influences such as termites influence the habitat and the occurrence of<br />
plant species.<br />
The soil and its profile are of importance as they are the growth medium for the plants,<br />
supplying nutrients and physical support.<br />
© Ecological Associates/ <strong>Marloth</strong> <strong>Park</strong> 27