Select an Issue from the Menu


STATE
OF CONSERVATION OF THE NATURAL ENVIRONMENT

health1.gif (3043 bytes)

The importance of development has always preceded that of the environment. This mentality has been slow to change but with the creation of various laws and policies that protect the environment, people will have to become more sensitive and aware of the environmental situation in Greater Johannesburg. The agricultural and conservation potential of the area is still untapped.
  • Analysis of conservation: Ridges run from east to west through the  central parts of the metropolitan area. The single biggest rock formation of the area is the Witwatersrand ridge, which stretches  from Orange Grove in the east to Roodepoort in the west. This ridge supports interesting indigenous flora such as the Redleaved Rock Fig Ficus ingens and Cape Gardenia Rothmannia capensis (Butchart, 1995). Smaller ridges are found to the south of Johannesburg and south of Lenasia. Exposed cliffs of the Northcliff Hill and Witpoortjie Falls, are home to Rock Dassies, and the latter to a pair of Black Eagles. Mostly out of reach of veld fires and man's activities, these cliffs support some ancient trees, such as Wild Olive Olea europea and Jacket Plum Pappea capensis, which may have been alive since 1886. Natural features, as well as protected and proclaimed conservation areas, can also be found alongside these ridges. Protected and proclaimed areas are seen around Roodepoort stretching eastwards to the northern areas of Johannesburg. Protected areas are also found in the far northern areas of the metropolitan area, as well as to the north, east and south of Randburg, Sandton and Alexandra. Other protected areas and natural features stretch from east to west along ridges and rivers to the south of Johannesburg. Some protected areas occur in Soweto; around the Klip River north of Lenasia, and natural features are found to the south of Lenasia and north of Ennerdale. Exposed rocks in the Klipriviersberg are home to many mammals, birds, reptiles, and rock-adapted plants such as Mountain Aloe Aloe marlothii and Transvaal Milkplum Englerophytum magalismontanum (Butchart, 1995). Pans and dams are mainly situated in the Klip (south) and Jukskei (north) River Systems. Wetlands in and around Soweto, including the large Olifantsvlei wetland to the southeast, are very important as conservation areas, but are being filled up or threatened by illegal dumping. A protected area is also located around Orange Farm. Conservation areas are only found on the outskirts and alongside ridges and rivers in the metropolitan area.
  • Environmental conservation areas in the northern suburbs of Johannesburg are located mainly alongside river systems, with very few if any around the CBD. There is a large conservation area to the west of Dobsonville, and a few around the Klip River system through Soweto. Large conservation areas are found around Kibler Park, with a very important area around the Klip River in the south. Other conservation areas are seen north of Lenasia, north and south of Ennerdale, and east of Weilers Farm. These areas are all "no go" areas for development.
  • The major business nodes are concentrated in the northern half of the metropolitan area to just south of the Johannesburg CBD. Environmental corridors in the north are all found alongside the Jukskei River system, except for the large conservation area in the far north. A very large and important corrridor can be seen along the Klip River in the south stretching from east to west to the south of Kibler Park. Some environmental corridors are also found south of Ennerdale and south of Lenasia.
  • Natural Grasslands, which once covered much of the Greater Johannesburg area, are now very scarce (Butchart, 1995). Those that still exist are mainly covered by indigenous Rooigras Themeda triandra . Most grasslands have however been disturbed by man's activities, and aliens like Khakiweed Tagetes minuta and Blackjack Bidens pilosa have taken over. Roadsides in Johannesburg are favourable for colonisation by Cosmos Bidens formosa, which flowers in autumn. Areas of savanna are found in various localities, but mainly in the Klipriviersberg, Melville Koppies and along the western end of the Witwatersrand ridge. Two distinct forms are present: acacia savanna, dominated by Common Hookthorn Acacia caffra and usually growing on north-facing slopes; and protea savanna, dominated by Common Sugerbush Protea caffra and typical of south-facing slopes (Butchart, 1995). Various grasses, including Guinea Grass Panicum maximum, grow beneath these trees. In other areas where the savanna have been disturbed, invasive aliens like Black Wattle Acacia mearnsii and Prickly Pear Opuntia ficus-indica flourish. Only where stream banks have been left undisturbed, do fragments of the species-rich riverine forest habitat of Johannesburg remain. The best example is found along the Witpoortjie River in the Witwatersrand Botanical Gardens, where large Stinkwood Celtis africana and River Bushwillow Combretum erythrophyllum are the dominant trees.
  • Efforts are being made to conserve water through media education by the Water Board, and the installation of safer and more effective water management strategies. These strategies have achieved positive results in some areas, but the lack of water provision in all communities still poses a problem.
  • The existing trees and shrubs of the Greater Johannesburg Metro Region follows (Kruger, 2000):

INDIGENOUS

Acacia caffra Common hook-thorn
Acacia hebeclada Candle thorn
Acacia karroo Sweet thorn
Acacia robusta Splendid thorn
Acacia sieberana Paperbark thorn
Acacia xanthophloea (P) Fever tree
Acalypha glabrata Forest false nettle
Acokanthera oppositifolia Common poison bush
Asclepias fruticosa Milkweed
Bolosonthus speciosus (P) Tree wistaria
Brachylaena rotundata Mountain silver oak
Buddleja saligna False olive
Buddleja salviifolia Sagewood
Canthium mundianum Rock alder
Carissa bispinosa Num-num
Cassine burkeana Transvaal kooboo berry
Celtis africana White stinkwood
Clerodendrum glabrum White cat's whiskers
Combretum erythrophyllum River bushwillow
Combretum molle Velvet bushwillow
Combretum kraussii (P) Forest bushwillow
Cryptolepis oblongifolia  
Cussonia paniculata Mountain cabbage tree
Dias cotonifolia (P) Pompon tree
Dichrostachys cinerea Sicklebush
Diospyros austro-africana (P) Jackal-berry
Diospyros lycoides Transvaal bluebush
Diospyrus whyteana Bladder-nut
Dodonaea viscosa (P) Sand olive
Dombeya rotundifolia Common wild pear
Dovyalis zeyheri Oval kei apple
Ehretia rigida Puzzle bush
Englerophytum magalismontanum Stamvrug
Erythrina lysistemon (P) Common coral tree
Euclea crispa Blue guarri
Ficus ingens Red leaved rock fig
Fraidherbia albida (P) Ana tree
Grewia occidentalis Cross-berry
Halleria lucida Tree fuchsia
Harpephyllum caffrum (P) Wild plum
Heteromorpha trifoliata Parsley tree
Kiggelaria africana Wild peach
Landolphia capensis Wild apricot
Lannea discolor Livelong tree
Leucosidea sericea Ouhout
Lippia juvanica Fever tea
Maerua cafra Bush-cherry
Maytenus heterophylla Common spike thorn
Maytenus polyacantha Kraal spike thorn
Mandulea sericea Cork bush
Nuxia congesta Wild elder
Olea europaea subsp. africana Wild olive
Ozoroa paniculosa Common resin tree
Pappea capensis Jacket plum
Parinari capensis Sand apple
Pavetta gardeniifolia Common bride's bush
Peltophorum africanum Weeping wattle
Pittosporum viridiflorum Pittosporum
Podocarpus spp. (P) Yellowwoods
Protasparagus laricinus Wild asparagus
Protasparagus suaveolens Cat thorn
Rhus dentata Nana berry
Rhus discolor Grassveld currant
Rhus dura Hard-leaved taaibos
Rhus lancea Karee
Rhus leptodictya Mountain karee
Rhus pendulina (P) White karee
Rhus pyroides Common wild currant
Rhus undulata Kuni-bush
Rothmania capensis Common rothmania
Schotia brachypetala Wheeping boer-bean
Salix mucronata Vaal willow
Sarcostemma viminale Caustic bush
Scolopia zeyheri Thorn pear
Strychnos pungens Spine-leaved monkey orange
Tapiphyllum parvifolium Mountain medlar
Tarchonanthus camphoratus Camphor bush
Vangueria infausta Wild medlar
Zanthoxylum capense Small knobwood
Ziziphus mucronata Buffalothorn
Ziziphus zeyheriana Dwarf buffalothorn

EXOTICS

Acacia dealbata Silver wattle
Acacia mearnsii Black wattle
Acacia podalyriifolia Pearl acacia
Acacia spp. Wattle
Agave americana American agave
Caesalpinia decapetala Mauritius thorn
Cortaderia jubata Pawpas grass
Cereus jamacaru Queen of the night
Eucalyptus grandis Bluegum
Eucalyptus spp. Gums
Jacaranda mimosifolia Jacaranda
Lantana camara Lantana
Ligustrum spp. Privets
Melia azedarach Persian lilac
Morus alba White mulberry
Nerium oleander Oleander
Nicoteana glauca Wild tobacco
Opuntia ficus-indica Prickly pear
Pinus spp. Pines
Populus spp. Poplars
Pyracantha spp. Firethorns
Ricinus communis Castor-oil plant
Robinia pseudoacacia Black locust
Rubus rigidus Bramble
Salix babylonica Weeping willow
Sesbania punicea Brazilian glory pea
Solanum mauritianum Bugweed
(P) = Planted trees, not found locally
  • The situation in the EMSS (EMLC, 1997) is as follows: 
    • Vegetation: residential population densities vary from high in Hillbrow and Alexandra, to medium in Inner City suburbs, and low in Houghton, Hyde Park and Sandhurst. The majority of trees are found in the low-density areas, while the high-density areas are almost devoid of trees. Prior to urban settlement, the area was a fire sub-climax area. Mostly indigenous trees and woodland growth could be found, but due to fires, the growth of seedling trees is inhibited, and grasslands now dominate the area. Some indigenous tree species still survive along streams, like the River Bushwillow, and on ridges and koppies, like proteas and acacias, where fires die out due to a lack of fuel. Vegetation differs according to rainfall and geology. Granites in the Lonehill and Norscot areas, are rich in nutrients, and a variety of vegetation can be found there. In contrast, the leached soils from shale rocks, support limited vegetation, while the well drained, shallow soils of the quartz Rietfontein Ridge supports a fire-resistant protea community. At least 50 species of trees and shrubs occur naturally in the EMLC, and at least one, the Honey-scented Protea is in danger of complete elimination. Alien vegetation includes the Black Wattle (Acacia mearnsii), Grey Poplar, Sesbania trees, and Kikuyu grass.
    • Birds: original highveld birds have adapted well in the urban environment. The Olive Thrush and Puffbacks originating in woodland have now invaded suburban gardens. Fruit eating birds like Grey Louries, Barbets, Mousebirds and Bulbuls have thrived in the urban environment. Larger birds such as the Spotted Dikkop and Crowned Plover, as well as grassland species such as Larks and Pipits have however declined. Raptors and fish-eating species have also declined.
    • Mammals: Only a few of the past free-roaming herds of game still exist. Dassies are still found in the Lonehill Tor, while housing and predation by domestic animals have depleted most natural habitats and species. Some bats, hares and meercats can still be found, while antelope have been reintroduced into conservation areas such as Rietfontein.
    • Reptiles: Some lizards, snakes and tortoises can still be found on koppies, ridges and in gardens.
    • Frogs: Water scarcity and weather uncertainties have caused breeding adaptations in frogs. The Guttural Toad and Common River Frog can be found in garden ponds, while bullfrogs and sand frogs only start breeding once the summer rains fall.
    • Fish: Very few fish species are left, due to water pollution and the construction of concrete sewers and canals. Fish types include eels, yellowish, minnows, mudsuckers, catlets and barbels.
    • Insects, butterflies, moths and arachnids: Insects are the most widespread and abundant of all animal groups on earth, and a large variety such as flies, mosquitoes, grasshoppers and locusts are found in the EMSS. Of the 29 insect families in the EMSS, 8 are butterflies and the remainder moths. Spiders, scorpions, ticks and mites are common in these areas.
  • The status of the natural environment in the SMSS is as follows:

- A significant loss of agricultural land and natural systems has taken place due to urban expansion.

- The Klip River Wetlands and Klipriviersberg are under severe pressure from urban encroachment and poor management. The Klip River and its wetland has very high conservation potential for ecological maintenance and recreational importance.

-Most of the region’s natural species has been replaced by exotic species (SMLC: LDO, 1997).

Conservation and recreational land use in the WMLC make up 2,8% of the area. The northern areas are environmentally more protected and maintained than the southern areas due to:

-the natural conditions of the area;

-the wealthier communities; and

-the previous allocation of resources.

These areas offer excellent opportunities for open space and integrated environmental planning, including the Witwatersrand Botanical Gardens, the Kloofendal Reserve, and the Florida Lake / Fleurhof Dam area (WMLC, 1997).

  • The NMLC consists predominantly of a series of rolling plains with low relief. Several small hills and dykes punctuate the generally flat topography. Features of the natural environment, are:

Geology: A basement complex of granites and gneisses, mafic to ultra-mafic rocks and intrusive dykes.

Natural vegetation: Bankenveld (A61) in Acocks (1988) or now in the new classification the Rocky Highveld Grassland (Low & Rebelo, 1996). Rocky hills carry bushveld dominated by Acacia caffra (common hook thorn), Celtis africana (white stinkwood), Protea caffra (sugar bush) and Olea europaea.

Exotic species: Their spread has been very successful, leaving only a few islands of indigenous species.

Birds: The hills, dykes, Protea veld and grassland patches support the naturally occurring bird species. Birds also flock to the artificial wetlands, dams, plantations and gardens.

Reptiles: A variety still remains in the area, such as the bullfrog. They breed in shallow rain-filled ponds as found, for example, in the Lanseria area.

Mammals: Destruction of their habitat through development has substantially reduced their diversity.

  • In the 1970’s the northern areas of the NMLC, towards Lanseria, were identified as potential Green Belt areas. The Green Belts were planned to provide open areas for city dwellers, barriers for the formation of conurbations, and green lungs to limit air pollution. Development to the north of the NMLC will impact on the possible formation of a Green Belt in the northern parts of the urban fringe (NMLC: LDO, 1997).
  • Areas available for conservation, recreation and tourism in the NMLC range from the southern boundary at Pimville to the north (Lanseria/Diepkloof): the golf course south of Pimville, the Orlando Dam and Pimville Dam, Noordgesig Hill, Eskom Powerline Servitude, Noordgesig Stream and Wetlands, Hill south of Powa Park, Green Belt east of Powa Park, Vlei area in Pimville, Freedom Square, Orlando community hall, the swamps in Bosmont, Consolidated Main Reef Gold Mine, West Park cemetery, Jan van Riebeeck Park, Melville Koppies Nature Reserve, Alberts Farm, rivers and streams, Northcliff Ridge, Emmarentia Park, Westdene Park, Braamfontein Spruit, Randpark Ridge, Jacaranda Park, Lion Park, Kya Sands sport fields, Honeydew club, community centers in Blairgowrie, Ferndale, Fontainbleau, Boskruin, Ferndale Reserve, Darrenwood dam and koppie, Windsor Golf club, Boschkop Nature Reserve, Kelland Bird Sanctuary, Golden Harvest Koppie, Diepsloot Nature Reserve, Hy-Many House, Olivedale Windmill, Zandspruit, North Riding Dyke, Delta Park, Waterfowl Bird Sanctuary, Jukskei Park, Northgate Koppie, Boskruin Koppie, Witkoppen Farm House, Norscot House, Pampoenspruit, President Ridge, Klipspruit and the Dainfern Golf Course.
  • The topography of the WMSS is characterised by ridges that represent one of the greatest natural environmental resources in the area. These ridges have great aesthetic, scenic, environmental and spiritual meaning and value. It also has the potential to be developed as open space corridors that provide a variety of amenities such as attractive views, open space preservation, passive recreation and conventially located recreational opportunities (WMLC, 1997).

REFERENCES

Acocks, J.P.H. 1988: Veld Types of South Africa. Botanical Research Institute: Pretoria.

Butchart, D. 1995: Wild about Johannesburg: All-in-one guide to common Animals and Plants of Gardens, Parks and Nature Reserves.Southern: Halfway House.

Kruger, J. 2000: Indigenous and Exotic Trees and Shrubs of Greater Johannesburg. EMSS - Urban Environmental Management - Personal Communication: Sandton.

Low, A.B. & A. Rebelo 1996: Vegetation of South Africa, Lesotho and Swaziland. DEAT: Pretoria.

SMLC, EMLC, NMLC, WMLC 1997: Land Development Objective.

WMLC 1997: Draft Development Policy for the main ridges within the WMLC area. WMLC: Roodepoort.

 

The Geographic Information files are WinZiped and  best viewed with ArcExplorer - (Click to download)

Unep United Nations unep. ceroi Ugland Publikit icleilogo.gif (1313 bytes)
wpe9.jpg (4277 bytes)

Home Page   Java Navigation

wpe9.jpg (4277 bytes)

Please Reference the Copyright with the Greater Johannesburg Metropolitan Council.
For problems or questions regarding this web contact  the Web Editor. Matthew 4:19
Last updated: March 02, 2000.
Thanks for visiting, you are visitor number:Hit Counter