Marloth Park Management Plan. - Nkomazi Local Municipality
Marloth Park Management Plan. - Nkomazi Local Municipality Marloth Park Management Plan. - Nkomazi Local Municipality
Frost Moderate frost - screen minimum less than 0 ºC - occurs in 15 percent of the years, with a mean frost season length of 2 days. Frost may be expected to occur during the winter months of June and July. Wind The wind speed and direction recorded at the Friedenheim weather station (Station number: 0555866 5; Latitude: 25º26' South; Longitude: 30º59' East; Altitude: 671 m a.s.l.) over a period of 30 years, was computed to determine the prevailing wind direction and average wind velocity. The most prevailing wind direction was determined as northeast, with an average directional frequency of 147 per thousand. The highest monthly average velocity recorded was 4.5 m.s -1 . VEGETATION The environmental attributes largely determine the graphical distribution of plant species and plant communities. A knowledge of the physical environment is thus a prerequisite for the understanding and ecological interpretation of plant communities identified during vegetation surveys. Marloth Park is situated in the lowveld, dominated by tropical bush and savanna veld types. This veld type occupies the plains between the eastern foot of the Drakensberg and the western foot of the Lebombo Range, where altitudes vary from 150 to 600 m above sea level. A large number of plant species are present, especially in the valleys and on rocky hills with sandy soils. The dominant trees are knob thorn Acacia nigrescens, marula Sclerocarya birrea subsp. africana, giant raisin Grewia hexamita, weeping wattle Peltophorum africanum, sickle bush Dichrostachys cinerea, common resin tree Ozoroa paniculosa, caterpillar bush Ormocarpum trichocarpum, red bushwillow Combretum apiculatum and silver cluster leaf Terminalia sericea. The grass layer is mixed and on the sour side, with iron grass Aristida diffusa subsp. burkei, hairy trident grass Tristachya leucothrix, broad-leaved bluestem Diheteropogon amplectens, weeping love grass Eragrostis curvula, broad-leaved panicum Panicum deustum, hairy love grass Eragrostis trichophora, herringbone grass Pogonarthria squarrosa, velvet signal grass Brachiaria serrata, common thatching grass Hyparrhenia hirta and red grass Themeda triandra as the dominant species. A profusion of forbs such as wild basil Ocimum canum, Oxygonum dregeanum, Felicia muricata, Rhynchosia densiflora, Zornia milneana, meidebossie Waltheria indica and spiny sida Sida alba are also found in this vegetation type. © Ecological Associates/ Marloth Park 23
INTRODUCTION VEGETATION CLASSIFICATION ON MARLOTH PARK When exploiting an area for financial benefit, the preservation of the environment and sustainability of natural resources must be assured, by implementing a sound management plan and a monitoring programme to determine the effects of applied management techniques. Sound ecological principles should be the basis for any effective planning. A functional ecosystem is characterised by interaction between its abiotic and biotic components, including a flow of energy and biochemical cycles. These components can be measured qualitatively or quantitatively as variation in climate, geology, soil, drainage, water regime, topography, animals, fire, and disturbance. Vegetation is the base of the trophic pyramid in the ecosystem as it converts solar energy through photosynthesis and makes this energy available for other organisms. Vegetation has a huge influence on the ecosystem, and in itself is mainly driven and determined by the physical and biological environmental factors of the ecosystem. Because of this, ecosystem types are usually determined according to different vegetation types that are recognised by variation in composition and structure. In the different vegetation types smaller patterns are distinguished in the landscape indicating different plant communities. These are defined as groups of associated plant species occurring in their peculiar habitat characterised by a relatively uniform physiognomy or appearance. A plant community, therefore, reflects local environmental and vegetation variation of an area. Recording the habitat data such as soil, water regime, aspect, and geography as well as species composition can facilitate the identification of a plant community. Major distinctions for plant communities are made on the basis of physiognomy or growth form of the vegetation, which are qualitative properties. Furthermore, a plant community can be quantitatively described in terms of density, frequency, cover estimation and biomass yield. The species composition of the plant community is determined by identifying all plant species in a defined area that is considered to be representative of the vegetation. This is done as plant communities represent homogenous vegetation units. Within each homogenous vegetation unit, the probability to find a specific plant species at a definite place is more or less similar for the whole community. Climate, landscape, soil and plant species composition in this area are homogeneous to such extend that it will have the same grazing and browsing value, and potential for plant biomass production. © Ecological Associates/ Marloth Park 24
- 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: A 610.1 B 104.0 C 7.4 D 19.9 E 39.8
- Page 33 and 34: METHOD For an initial and broad sca
- Page 35 and 36: RESULTS AND DISCUSSION Analysis and
- 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
INTRODUCTION<br />
VEGETATION CLASSIFICATION ON MARLOTH PARK<br />
When exploiting an area for financial benefit, the preservation of the environment and<br />
sustainability of natural resources must be assured, by implementing a sound management<br />
plan and a monitoring programme to determine the effects of applied management techniques.<br />
Sound ecological principles should be the basis for any effective planning.<br />
A functional ecosystem is characterised by interaction between its abiotic and biotic<br />
components, including a flow of energy and biochemical cycles. These components can be<br />
measured qualitatively or quantitatively as variation in climate, geology, soil, drainage, water<br />
regime, topography, animals, fire, and disturbance.<br />
Vegetation is the base of the trophic pyramid in the ecosystem as it converts solar energy<br />
through photosynthesis and makes this energy available for other organisms. Vegetation has a<br />
huge influence on the ecosystem, and in itself is mainly driven and determined by the physical<br />
and biological environmental factors of the ecosystem. Because of this, ecosystem types are<br />
usually determined according to different vegetation types that are recognised by variation in<br />
composition and structure.<br />
In the different vegetation types smaller patterns are distinguished in the landscape indicating<br />
different plant communities. These are defined as groups of associated plant species occurring<br />
in their peculiar habitat characterised by a relatively uniform physiognomy or appearance. A<br />
plant community, therefore, reflects local environmental and vegetation variation of an area.<br />
Recording the habitat data such as soil, water regime, aspect, and geography as well as<br />
species composition can facilitate the identification of a plant community. Major distinctions<br />
for plant communities are made on the basis of physiognomy or growth form of the<br />
vegetation, which are qualitative properties. Furthermore, a plant community can be<br />
quantitatively described in terms of density, frequency, cover estimation and biomass yield.<br />
The species composition of the plant community is determined by identifying all plant species<br />
in a defined area that is considered to be representative of the vegetation. This is done as plant<br />
communities represent homogenous vegetation units. Within each homogenous vegetation<br />
unit, the probability to find a specific plant species at a definite place is more or less similar<br />
for the whole community. Climate, landscape, soil and plant species composition in this area<br />
are homogeneous to such extend that it will have the same grazing and browsing value, and<br />
potential for plant biomass production.<br />
© Ecological Associates/ <strong>Marloth</strong> <strong>Park</strong> 24