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C R Hurt K G T Camp Vegetation
Structure and Compositions
VEGETATION STRUCTURE AND COMPOSITION The vegetation of these areas is mainly a savanna of varying tree and bush density. The vegetation is characterized by an open to dense scrub forest containing many species of Euphorbia. Semi-deciduous bush is found in the dry, hot areas of the valleys. The vegetation in most of these areas has been altered by severe disturbance (overgrazing and cultivation) and this has caused a break down in the natural resources. Pioneer species dominate and erosion is severe with extensive areas eroded to the parent material. Many species are deciduous during the winter but species like Boscia albitrunca, Euclea crispa, E. schimperi and Olea europaea subsp. africana remain evergreen. Acacia species such as Acacia robusta, A. karroo, A. nilotica, A. tortilis, A. gerrardii and A. ataxacantha are common. A major contributor to the problem of bush encroachment is Acacia tortilis, and this species forms dense thickets, particularly on abandoned lands at lower elevations. The climax grasses are Themeda triandra var. trachyspathea, Heteropogon contortus, Bothriochloa insculpta, Setaria incrassata (the latter two on black clays) and Cymbopogon plurinodis. In the shade the dominant grasses are Panicum maximum and P. deustum. Subclimax grasses include Eragrostis curvula, E. chloromelas, and Digitaria spp. Species found in the severely overgrazed areas are Aristida congesta, A. diffusa, Chloris virgata, Melinis repens, Tragus beteronianus and Urochloa mosambicensis. Mixed succulent scrub is found on dry, north-facing aspects on shallow soils. These areas have a low rainfall and are relatively free of frost. A Euphorbia tirucalli community grows on arid, alkaline soils. Thickets occur, often on old lands, from which other species are excluded. Euphorbia triangularis frequently grows in association with Euphorbia tirucalli on dry, north facing aspects and tends to grow in a belt across the slope. Basal cover is very poor and Panicum maximum and P. deustum provide sparse cover. Euphorbia ingens grows on frost free slopes and on the floors of the lower valleys where frost does not occur. Combretum apiculatum Tree veld grows on shallow, rocky soils on dry north-facing aspects. It is typically an open woodland but overgrazing has resulted in an invasion by species such as Euphorbia tirucalli, E. grandicornis, E. pseudocactus and Acacia species. Sclerocarya-Acacia Tree Veld grows at elevations below 600 m in an area of light frosts, with moderately severe frosts occurring occasionally. Soils are generally deep. The dominant tree is Sclerocarya birrea while Acacia sieberana is found at the upper elevational range. Disturbance has resulted in an increase in Acacia nilotica, A. tortilis and Dichrostachys cinerea. The grass layer is dominated by secondary species due to disturbance and the commonest grasses are Aristida congesta var. barbicollis, Bothriochloa insculpta, Chloris gayana, C. pycnothrix, C. virgata, Cymbopogon plurinodis, Cynodon dactylon, Eragrostis chloromelas, E. racemosa, E. superba, Heteropogon contortus, Melinis repens, Melinis nerviglumis, Panicum maximum, Perotis patens, Setaria incrassata, Setaria sphacelata, Sporobolus fimbriatus, Sporobolus pyramidalis, Themeda triandra var. trachyspathea, Tragus berteronianus, Trichoneura grandiglumis and Urochloa mosambicensis. Spirostachys Woodland occurs mainly on hot, dry north-facing aspects and is particularly extensive in the Mvoti and Mgeni River valleys. Erosion is severe, mainly on colluvial and alluvial soils which are neutral to alkaline. The vegetation is severely disturbed and the woodland has been generally replaced by secondary vegetation with relic trees remaining. The dominant grasses indicate the severe disturbance. They include Aristida barbicollis, Bothriochloa insculpta, Cynodon dactylon, Eragrostis superba, Melinis repens, Melinis nerviglumis, Tragus beteronianus and Urochloa mosambicensis. The climax grasses are presented by Cymbopogon plurinodis, Heteropogon contortus and Themeda triandra var. trachyspathea. Lowveld (BRG 22) On heavy clay soils the dominant grass species of the sweetveld are the tall form of Themeda triandra, Aristida bipartita, Bothriochloa insculpta, Cymbopogon excavatus, Digitaria spp., Diplachne eleusine, Eragrostis superba, Setaria incrassata and Sporobolus fimbriatus. Panicum maximum and Panicum deustum grow in the shade of trees. Themeda triandra is less common on sandy soils where Aristida diffusa, Brachiaria nigropedata, Cymbopogon excavatus, C. plurinodis, Elionurus muticus, Eragrostis curvula, E. superba, Eustachys paspaloides, Heteropogon contortus, Hyparrhenia hirta, Panicum coloratum, Pogonarthria squarrosa and Sporobolus fimbriatus are among the common grass species. Sandy Bushveld (BRG 23) Terminalia sericea, Combretum molle, Acacia burkei, Strychnos spp., and Albizia versicolor grow in the woodland areas. Grass cover is sparse and the species reflect the sandy nature of the soil including Hyperthelia dissoluta, Pogonarthria squarrosa and Perotis patens. Other grasses found are Aristida spp., Themeda triandra, Urochloa mosambicensis, Digitaria spp., and Aristida spp. The Palm Veld, which lies to the east of the Sand Forest zone, also has a patchy appearance. The palms consist of Hyphaene natalensis and Phoenix reclinata in a bush clump grassland which includes Themeda triandra, Perotis patens, Eragrostis spp. and Aristida spp. amongst others. The trees, Mimusops caffra, Syzygium cordatum, Albizia adianthifolia, Acacia robusta, Spirostachys africana and Schotia brachypetala grow on drained raised ground. In the moist depressions grass-sedge com-munities are found.
Benchmark sites for the Valley Bushveld (BRG 21) and the Lowveld (BRG 22) are presented in Tables 1 and 2 respectively. Due to the considerable influence of landscape position on species composition in the Lowveld, benchmarks for upland, midslope and bottomland areas are presented in Table 2 for the Lowveld vegetation type. No benchmark has been described for the Sandy Bushveld (BRG 23). Tables 1 and 2 also present other grass species which occur in these Bioresource Groups, but are not necessarily found in the benchmark. The species groupings (i.e. Increaser and Decreaser species), and concepts related to this classification, are explained in detail in Production Guidelines 6.1 to 6.3 in this series. Veld that consists predominantly of redgrass, with Panicum maximum (Guinea grass, ubabe) under the trees, is considered to be in excellent condition. Indicator species for Bioresource Groups 21 and 22 are presented together with their weightings in Table 3. These weightings can be used in the Weighted Key Species method for assessing veld condition (refer to Production Guideline 6.2 in this series for a description of this method).
Neither sheep nor dairy cattle are suited to these warm areas. Sheep suffer from a variety of diseases, while the high temperatures and the extensive nature of farming do not suit dairy production. Beef and game farming are, however, well suited to the region. Because the veld is sweet, grazing is provided for the beef breeding herd throughout the year, without the need for supplementation. Livemass gains in steers will, where sufficient grazing is available, average as much as 0.6kg/day through the year. Weaners of 240 to 260kg can be produced at 8 to 9 months of age. Goat farming is not popular in this region, but the potential for goats is relatively high where good browse is available. Goats will need to be provided with good sweetveld grazing in winter in those areas in which the majority of browse-producing plants are deciduous (i.e. lose their leaves in winter). Goats in these regions have two major advantages. Firstly, a browsing system is usually superimposed on a grazing system, and therefore major reductions in grazer stocking rates are unnecessary. This effectively increases the red meat production per unit area. Secondly, goats are able to control bush efficiently, and this reduces the management costs (e.g. bush control costs such as herbicides, fire, mechanical clearing - refer to Production Guideline 7.7 in this series). The bushveld areas of KwaZulu-Natal therefore have much potential for extensive animal production. Due to the nature of the vegetation, however, maximal animal production can be achieved only in conjunction with good veld management.
VELD MANAGEMENT NORMS AND GENERAL INFORMATION FOR BRG’s 21, 22 & 23: VALLEY BUSHVELD, LOWVELD AND SANDY BUSHVELD
1 In areas where stocking rates are higher than those given for potential grazing capacity, the livestock production potential will not be achieved. This is particularly so where continuous grazing is practised. 2 Current grazing capacity is based on the average condition of veld in the BRG as estimated in 1997. 3 Animal Unit (AU) grazing days per hectare are based on the estimated average CGC of the BRG. 4 Livestock production potential refers to the expected amount of live mass (kg) gain per hectare using a beef weaner production system (see the example of such a system in Production Guideline 2.6).
Table 1. Benchmark species abundances and species not occurring in the benchmark for grassland in Valley Bushveld (BRG 21).
Table 2. Benchmark species abundances and species not occurring in the benchmark for grassland in Lowveld (BRG 22), in upland, midslope and bottomland sites.
Table 3. Proposed key grass species and species weightings for grassland in Valley Bushveld and Lowveld (BRG’s 21 & 22).
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