Information sheet for the site designated to the
List of Wetlands of International Importance
in terms of the
Convention on Wetlands of International Importance
especially as Waterfowl Habitat
DATE OF COMPILATIONOriginally completed: October 1990
Updated: October 1995
Not yet available
COMPILEROriginally compiled by:
Dr Robert Kyle
Fisheries Research Officer
PO Box 43
South Africa Tel (035) 5721011
Fax (035) 5721011 Updated by:
a) M.C. WARD
b) Dr. R. KYLE a) Private Bag X314
3974 b) Fisheries Research Officer
PO Box 43
South Africa Tel (035) 5721011
Fax (035) 5721011
NAME OF WETLAND
DATE OF RAMSAR DESIGNATION
28 June 1991
GEOGRAPHICAL CO-ORDINATES27o 15' S - 27o 25' S
32o 32' E - 32o 44' E Map number: 1:50000 2732 BC & BD SIBAYI
430 km north east of Durban
Richards Bay - 165 km south
9.1 Boundary Integrity
Q (Freshwater lake: permanent)
ALTITUDEMin: 20 m
Max: 20 m
Max depth: 43 m
OVERVIEW OF SITE
Lake Sibaya is situated on the seaward margin of the low-lying Mozambique Plain in eastern Maputaland. The lake is bedded on Tertiary marine deposits overlying Cretaceous to Palaeocene sediments and is narrowly separated from the sea by a range of high afforested coastal dunes. The remainder of the area is composed of recent reworked sands situated between Manzengwenya and Mbazwane plantations, to the west is Mseleni. Marine canyons offshore of Lake Sibaya suggest that the lake was previously connected to the sea by a large river, possibly the Pongolo which is presently diverted northwards to Delagoa Bay.
Between the eastern shore and the sea is a range of high dunes attaining altitudes of up to 165 m. To the west of the dunes the land is very flat, and consequently the boundary of the catchment feeding the lake is difficult to define. The total catchment area is estimated at 530 kmē, of which 60-70 kmē is taken up by the lake itself.
13.1 Geology and geomorphology
Lake Sibaya, situated on the coastal plain of Maputaland, is a landlocked freshwater lake of surface 60-70 kmē, elevated roughly 20 m above mean sea-level. The coastal plain is composed of Resent and Tertiary sands and Pliocene/Miocene beds overlaying Cretaceous mudstone.
Between the eastern shore and the sea is a range of high dunes attaining altitudes of up to 165 m. To the west of the dunes the land is very flat, and consequently the boundary of the catchment feeding the lake is difficult to define.
The occurrence of well developed sub-marine canyons is strongly suggestive of a former extension of the Pongolo River to an estuary at Sibaya in Pleistocene time, the existing lake presenting the former lagoon of the Pongolo River prior to the development of the river's present course northwards along the eastern foot of the Lebombo Range to join the Ingwavuma and Usutu rivers to form the Maputo River.
The chief mechanism by which water is lost from the lake is by evaporation, but it is suspected that a relatively small amount may be lost from the lake by seepage to the sea.
13.4 Soil type and chemistry
In that the greater proportion of Maputaland comprises recent wind-redistributed grey sand, it soils are very sandy and thus are characterized by adverse physical and chemical properties which render them generally very infertile and of low potential agriculture capacity. In the high-rainfall eastern portion of Maputaland, the soils are also much leached which make makes them even more inherently infertile on dune areas.
13.5 Water quality
The lake water is clear with Secchi disc transparency averaging 3,2 m. The pH of the lake varies between 8,2 and 8,3. The main chemical characteristics are an elevated chloride level for fresh water (135 mg/l) and constantly high dissolvent oxygen concentrations.
13.6 Depth, fluctuations and permanence
Extreme states of Lake Sibaya over a sixty year period:
State Minimum Average Maximum Level (m above M.S.L.) 19.4 20.8 22.9 Area (kmē) 54.0 64.0 77.0 Volume (106 m3) 620.0 700.0 840.0 Mean depth (m) 10.9 10.9 11.5
13.7 Tidal variations
13.8 Catchment area
The total catchment area is estimated at 530 kmē, of which roughly 60-70 kmē is taken up by the lake itself.
13.9 Downstream area
13.10 ClimateMean annual precipitation (east) 1200 mm
Mean annual precipitation (west) 800 mm
Mean figure 1030 mm
Mean annual temperature for a year is 21,6 C, varying from 11,5 C in July to 28,7 C in January.
At Lake Sibaya Research Station relative humidity had maximum and minimum values of 88 and 56 percent respectively for the winter months and 83 and 60 percent for the summer months.
On the eastern side of Lake Sibaya is Dune Forest (Acocks Veld Type No. 1). Tinley (1958) recorded 147 species belonging to 52 families for the Dune Forest in the vicinity of Lake Sibaya. On the drainage lines leading into the lake, remnant swamp forest is found. Vegetation on the surrounding coastal sands is markedly diverse. On the eastern edge are tall dune forest trees, while the main dunes are covered by a shorter dune forest. Around the remainder of the lake a dry coastal forest occur. Open and closed woodland covers extensive areas of the surrounding area. High water-table grasslands and hygrophilous grasslands are found adjacent the lake.
The area is situated within rural KwaZulu. The surrounding area is administered by three different chiefs namely Zikhali, Nxumalo and Tembe.
15.1 Legal status
The entire proposed area is state land. The water surface was proclaimed as a Nature Reserve in terms of the KwaZulu Nature Conservation Act in 1994.
CONSERVATION MEASURES TAKEN
A start has been made on fencing the area, with an electric fence being erected around a third of the lake. In the long term, it is expected that the whole lake will be fenced and managed as a formally protected area.
Management by the Bureau is essentially limited to law enforcement, protecting the fauna and selected forest communities.
Alien plant control has taken place on the eastern shore, combating Pereskia aculeata.
Problem species control - hippopotamus/human conflicts are dealt with, either by stationing staff in problem areas to drive hippopotamus away from fields or, rarely to shoot animals.
The reserve is patrolled by well armed and trained staff on foot and by boat to ensure compliance with controls and legal restrictions.
16.1 Management plan
A management plan is in its final draft and will be submitted as soon as it is available.
Special aspects include the protection of fundamental ecological processes and the active involvement of the neighbours of the reserve in its management. The local communities are being made through appropriate tourism. Some pilot schemes are under way.
The reserve has only recently been proclaimed and little management has been undertaken except patrols to protect the larger mammals, particularly hippo and crocodiles.
CONSERVATION MEASURES PROPOSED BUT NOT YET IMPLEMENTED
- Need to control the numbers of herbivores using the grasslands, as severe overgrazing and veld degradation is occurring.
- Control on irrational burning throughout the year which is aiding veld degradation.
- Levels for sustained utilization of natural resources by local people need to be determined and enforced.
- Limited tourist activity to maintain the wilderness atmosphere of the area.
- Water surface is being proclaimed as a nature reserve.
CURRENT LAND USE
Surroundings and catchment
The area is situated within rural KwaZulu. Many of the people rely upon subsistence agriculture (following a shifting cultivation method). The area is heavily grazed by their livestock and natural resources are used in everyday routine.
Large plantations (mainly Pinus) were established to the south of the area (Mbazwana) and to the north (Manzengwenya).
18.1 Resource utilisation
Resources used by both local residents and recreational visitors include fish, reeds, sedges and wild fruits. Very little data is available on overall utilisation. Recently a permit was issued for gill-netting and all catches are monitored. Since the lake is not fenced or controlled the only accurate resource use monitoring is the legal gill-net fishery.
DISTURBANCES AND THREATS INCLUDING CHANGES IN LAND USE AND MAJOR DEVELOPMENT PROJECTS
Water extraction for Mbazwane and Vasi is under way with pumphouses being erected on the shores.
At one stage, Forestry considered floating logs from the plantation onto the lake to store them before transport from the region.
Due to its endorheic nature, the lake is particularly susceptible to pollution. Extensive DDT spraying for malaria control in the area is a cause of concern, while more recently, interest has been shown for spraying molluscacide in the wetlands to destroy the bilharzia snail (the poison will also kill invertebrates and even small fish).
Extensive cultivation has occurred in most of the drainage lines leading into the system, Agriculture in the catchment areas and drainage lines may well cause erosion, eutrophication and pollution.
The local residents belong to three different communities each of which is living at subsistence level at best. Many local people see forestry as a means of improving their standard of living. Overgrazing and injudicious burning are also problems.
Overexploitation of natural resources.
19.1 Present threats
HYDROLOGICAL AND BIOPHYSICAL VALUES
SOCIAL AND CULTURAL VALUES
The area is situated within rural KwaZulu. The area is under developed and therefore the people that live here, lead their lives to a large extend in a traditional way.
a) Zoo plankton
The major species are entomostracan crustacea - copepods and cladocerans. Rotifers are common; water mites an zoeue lavae of the benthic brown crab occur in moderate densities. Seasonally insect larvae and larvae of the fish Grilchristella aestuarius are abundant. One endemic copepod (Tropocyclops brevis) occurs in the Lake.
The main species are various Crustacea and Molluscs. Crustaceans dominated by burrowing amphipods and taniads. Larger crustaceans include the crab Hymenosoma orbiculare and a freshwater shrimp Caridina nilotica. Also found are various coelenterates, nematodes, a marine polychaete worm and many insect larvae (mayflies, chironomids, dragon flies, damsel flies, water bugs, water boatmen.) 15 Species of Mollusc in the waterbodies, with 43 species of terrestrial Mollusc in the adjacent dune forest.
Fifty six species of spiders identified in the area, 3 species of scorpion, 1 solifuge species, 5 pseudoscorpion species and 3 species of opiliones. Myriapods - 20 species.
Megaraneus campbell (Araneidue) only from Sibaya's eastern shore.
18 species occur in the lake and feeder streams; these are dominated by cichlids (4 species) and gobiids (3 species). The fauna reflect a marine origin and have close affinities with tropical forms. One goby (Silhouetta sibayi) has its largest known population in the lake as very few records of it have been received from other localities. The most successful and abundant fishes are Oreochromis mossambicus (Mozambique tilapia), Pseudocrenilabrus philander (southern mouth-brooder), Tilapia sparrmanii (banded tilapia), Clarias gariepinus (sharptooth catfish) and Glossogobius giuris (tank goby).
22 species of frog recorded from Lake Sibaya; 20 of these are tropical forms, 1 a "cape" form and the other a transitional species. Common species are reed frogs (Hyperolius spp.), grass frogs (Ptychadena spp.), Rana spp. and toads (Bufo spp.)
8 species are closely associated with Sibaya (these include Varanus niloticus (water monitor), Python sebae (African python), Lycodonomorphus r. rufulus (brown water snake), Natriciteres variegata sylvatica (olive marsh snake),Philothamnus r. irregularis (northern green water snake) P. hoplogaster (common green water snake), Naja melanoleuca (forest cobra) and Crocodylus niloticus (Nile crocodile)).
A further 59 species have been recorded in the adjacent area.
Red data species are:
VulnerableCrocodylus niloticus (Nile crocodile)
Varanus exanthematicus (veld monitor)
V. niloticus (water monitor)
Bradypodion setaroi (dwarf chameleon)
Bitis gabonica (gaboon adder)
RareLycophidion semiannule (eastern wolf snake)
Dasypeltis medici medici (tropical egg-eater)
279 bird species have been recorded for the Lake, 62 of which are closely associated with the lake through their breeding, feeding or roosting habits. The most numerous are red and white breasted cormorants (Phalacrocorax spp.). Other piscivores are Pied, Giant and Malachite Kingfishers (Halcyon sp.), Fish Eagles (Haliaeetus vocifer), variety of Herons, Darters and Egrets. Waders include White-fronted Sand Plover (Vanellus spp.), Black-winged Stilt (Himantopus himantopus), Avocet, Greenshank, Spoonbills and Herons, with Jacana, Crakes, Gallinules and Bitterns in sheltered bays.
Based on the 1984 Red Data Book - 6 species are vulnerable:Martial Eagle (Polemaetus bellicosus)
Stanley's Bustard (Neotis denhami)
Natal Nightjar (Caprimulgus natalensis)
African Broadbill (Smithornis capensis)
Pinkthroated Longclaw (Macronyx ameliae)
15 species are rare:Little Bittern (Ixobrychus minutus)
Pygmy Goose (Nettapus auritus)
Bat Hawk (Macheiramphus alcinus)
Rufousbellied Heron (Butorides rufiventris)
Palmnut Vulture (Gypohierax angolensis)
Ierser Black-winged Plover(Vanellus melanopterus)
Neergaard's Sunbird (Nectarinia neergaardi) while 6 species are Indeterminate: Flamingoes
Grass Owl (Tyto capensis)
Woodward's Batis (Batis fratrum)
Wattle-eyed Flycathcer (Platysteria peltata)
Yellow White-eye (Zosterops senegalensis)
6 mammal species are associated regularly with the Lake; these are white-tailed mongoose (Ichneumia albicauda), water mongoose (Atilax paludinosus), hippopotamus (Hippopotamus amphibius), reedbuck (Redunca arundinum), Vlei otomys (Otomys irroratus) and African marsh rat (Dasymys incomtus)
154 hippo's were in the lake in July 1988, with a 13 % infant composition.
Other mammals associated with the area include
VulnerableParaxerus palliatus tongensis (Tona red squirrel)
Neotragus moschatus (Suni)
RarePetrodromun tetradactylus (four-toed elephant shrew)
Cercopithecus albogularis (samango monkey)
Cephalophus natalensis (red duiker)
Cephalophus monticola (blue duiker)
A further 30 mammal species occur around the system, mostly rodents.
22.1 Species count
Hippo, crocodile are counted annually by helicopter and waterbirds are counted twice each year by vehicle and boat. The last count of all was in July 1995. The hippo and crocodile numbers have dropped over the last fifteen years due principally to poaching. Waterbird numbers have not shown any clear trends.
The aquatic vegetation consists of submerged macrophytes (such as Ceratophyllium demersum, and Myriophyllum spicatum), semi-emergent plants (such as Potamogeton schweinfurthii and Nymphaea capensis) and free floating aquatics, Pistia statiotes. Partially invendated, marginal vegetation consists predominantly of sedges (Scirpus littoralis, Cladium mariscus, Phynchospora spp.) with areas of Typha latifolia (bulrush) and Phragmites mauritianus (reeds).
On drainage lines leading into the lake, remnant swamp forest is found on a few of the streams. The trees are Ficus trichopoda (swamp fig), Voacanga thouarsii (Wild frangipani), Syzygium cordatum (waterberry) and Macovanga capensis (Wild poplar). Ferns are common in the swamp forest. The remainder of the drainage lines consist of hydrophilous grasses and sedges; besides those noted earlier, Cyperus spp. are common, with patches of Cyperus papyrus along a number of streams.
Vegetation on the surrounding coastal sands is markedly diverse and has a number of Red Data species. On the eastern edge are tall dune forest trees, (comprised of Chrysophyllum viridifolium)(fluted milkwood), Chaetachme aristata (thorny elm), Drypetes gerrardi (hairy drypetes) and Cassine spp. The main dunes are covered by a shorter dune forest with dominant trees being Croton gratissimus (Lavender croton), Mimusops caffra (red milkwood), Balanites maughamii (torchwood) Ziziphus macronata (buffalo thorn), Diospyros rotundifolia (dunejackal-berry), Drypetes natalensis (Natal drypetes) and Euclea spp. The understorey is commonly make up of stands of Isoglossa woodii and/or Acalypha glabrata (forest false-nettle).
Around the remainder of the Lake, other forest patches occur; these being a dry coastal forest type, with species of sand forest and coastal forest mixed. Characteristic species are Dialium schlechteri (Zulu pod-berry), Balanites maughamii (torchwood), Manilkara discolor (forest milkberry), Cleistanthus schlechteri (bastard tamboti), Craibia zimmermannii (small craibia), Croton spp. and Mimusops caffra (red milkwood), Hymenocardia ulmoised (red heartfruit), Aloe bainesii (tree aloe) and Ficus spp.
Open and closed woodland covers extensive areas of the surrounding area. Heavy grazing pressure and uncontrolled burning by local people have caused many of the grasslands to be encroached by scrub; common encroacher woody species are Parinari capensis (dwarf mobola plum), Salacia krausii, Eugenia mossambicensis, Dichrostachys cinerea (sickle bush) and Helichrysum kraussi. The woodland species consist of many edible types, such as Strychnos madagascariensis (black monkey orange), Strychnos spinosa(spiny monkey orange), Sclerocarya birrea (marula), Trichitia (Natal mahoganey), Hyphaene natalensis (Lala palm), Syzygium cordatum (waterberry) and Gareinia livingstonei (African-mangosteen). Other common woody species in the woodland are Albizia adianthifolia (flat-crown), Terminalia sericea (silver terminalia), Mundulea sericea (corke bush), Vangueria infausta (wild medlar) and Apodytes dimidiata (white pear).
Climbers are abundant in the woodlands and at margins of forest patches. The most common are Landolphia kirkii, Landolphia petersiana, Smilax kraussiana and Rhoicissus digitata.
As noted earlier, the coastal grasslands are being reduced through poor veld management. Grass species in the coastal grasslands and woodlands are Tristachya leucothrix, Trachypogon spicatus, Vrelytrum agropyriodes, Themeda triandra, Hypartenia filipendula, Cymbopogon excavatus, Digitavia natalensis, and Imperata cylindrica. A diverse forb component occurs in the grasslands, particularly evident after burning common species include Polygala sphenoptera, Polygala fryticosa, Zornia capensis, Gazania krebsiana, Pentanisia prunelloides, Lobelia pinifolia, a variety of composites, Wahlenbergia undulata, Stylosanthes fruticosa and Aeschynomene micrantha.
In old cultivated areas, the grass component is made up of Rhynchelytrum repens, Eragrostis capensis, Eragrostis ciliaris, Perotis patens and Panicum maximum.
High water-table grasslands and hygrophilous grasslands are found adjacent the lake and in depression in the surrounding area. Common grasses include Ischaemum arcualtum, Acrocera macrum, Stenotaphum secundatum and Dactyloctenium geminatum. Sedges are present in these communities; these include Cyperus spp., Fuirena spp., Pycreus spp and Scleria spp.
Associated with the Lake environment are freshwater pans in the coastal plain. Plant species are similar to those found in the sheltered bays of the Lake e.g. Potamogeton schweinfurthii, Nymphaea capensis, Nympoides indica and Utricularia spp. Ludwigia octovalvis and Polygonum spp. are common marginal forbs, while Typha latifolia, Echinochlora pyramidalis, Phragmites mauritianus and Cyperus papyrus are common. Wolffia arrhiza and Lemma minor are floating species in the pans.
Red data species in the area include:
VulnerableDiospyros rotundifolia (dune jackal-berry)
Encephalarios ferox (Tongoland cycad)
Warburgia salutaris (pepper-bark tree)
RareAncylanthus monteiroi (dune false medlar)
Blighia unijugata (triangle tops)
Bridelia cathartica (knobby bridelia)
Coffea racemosa (wild coffee)
Commiphora zanzibarica (Zanzibar commiphora)
Craibia zimmermannii (small craibia)
Dialium schlehteri (Zulu pod-berry)
Lasiodiscus mildbraedii (Losiodiscus)
Morus mesoaygia (African mulberry)
Pavetta gertneri (Zulu bride's bush)
Suregada zanzibariensis (woodland suregada)
Tapura fischeri (leaf-berry tree).
In addition the only population of Vanilla roscheri occurs near Lake Sibaya, while another orchid, Oecevelades decaryanum was collected at the Lake for the first time in the country and an unknown Oecevelades sp. occurs near Sibaya.
SCIENTIFIC RESEARCH AND FACILITIES
Since a Research Station was established at the Lake during the 1970's, hundreds of articles were written on a wide range of studies carried out in this time. Work was carried out on productivity, food chains, plant and animal surveys, fish dynamics, hydrological surveys, and general limnological research.
Animals collections have taken place around the lake since 1905 when the earliest fish collection were made.
Besides fish collections, a survey was carried out on aspects of the ecology of the lake by Tinley in 1958; he concentrated on the hippopotamus.
The highest lake level was experienced in 1943, many local roads were inundated and the flooding was serious enough to warrant evacuation of the Rhodes University research station. Since the research station was abandoned, research has focused on the hippo and crocodile populations, plant surveys in the surrounding areas, grazing impact of herbivores and annual aerial surveys (since 1984). Use of plant material is partly monitored.
Utilization of the fish resource has been considered and a project is underway.
Research into health hazards has taken place, aimed at Mseleni joint disease and schistosomiasis.
Geophysical and geological surveys have been undertaken.
24.1 Projects in progress
24.2 Projects just completed
24.3 New findings
24.4 Proposed new projects
The area would be most useful for extension programmes as it is accessible and thousands of people live in the surrounding area. Extension staff are involved continuously in the community and a conservation area would be most useful for demonstrating conservation principles in this rural area.
Once proper veld management and burning programmes can be implemented, the difference between the conserved area and adjacent land will be apparent and a valuable example for education.
Sustained use of natural resources can be implemented and used in educating the people on resource exploitation.
The re-introduction of game around the lake would provide an area for people to visit to see and learn about wild animals which used to occur in their area.
RECREATION AND TOURISM
The lake and surrounding area lends itself to development of small wilderness-type camps. Boat trips on the lake are feasible, while trails through the relatively undisturbed shore vegetation are most rewarding.
At this stage only 1 camp is in operation but a further 2 are envisaged. They would be linked by walking trails and the possibility exists for canoe trails.
A limited amount of recreational fishing is done but the size of fish in the system does not encourage most tourists to fish.
KwaZulu Bureau of Natural Resources
ALLANSON, B.R. (Ed) 1979. Lake Sibaya. Monographiae Biologicae 36: 1-364, W. Junk, The Hague.
BRANCH, W.R. (Ed.) 1988. South African Red Data Book - Reptiles and Amphibians. South African National Scientific Programmes Report no. 151.
BROOKE R. K. 1984. South African Red Data Book - Birds. South African National Scientific Programmes Report no. 97.
BRUTON, M.N. & K.H. COOPER (Ed) 1980. Studies on the Ecology of Maputaland. Rhodes University and Natal Branch of the Wildlife Society of Southern Africa.
DE MOORE, I.J. & BRUTON M.N. 1988. Atlas of translocated indigenous aquatic animals in Southern Africa. South African National Scientific Programmes Report no. 144.
HALL, A.V., DE WINTER, M., & S.A.M. OOSTERHOUT 1980. South African National Scientific Programme Report no. 45.
MACLEAN, G.L. 1985. Roberts' Birds of Southern Africa. The Trustees of the John Voelcker Bird Book Fund. Cape Town.
MEYER, R. DE BEER, H.J. & J. BLUME 1982. A geophysical-geohydrological study of an area around Lake Sibayi, northern Zululand. CSIR Geophysics Division Report, 32 pp.
SKELTON, P.H. 1987. South African Red Data Book - Fishes. South African National Scientific Programmes Report no. 137.
SMITHERS, R.H.N. 1986. Red Data Book - Terrestrial Mammals. South African National Scientific Programmes Report no. 125.
WALTER, G.J. & A.J. CRAIG 1983. List of birds seen in the Mkuze Game Reserve and at Lake Sibaya and at Manzengwenya in Tongaland. Unpublished list.
WRIGHT, C.I. 1957. Sedimentation of Lake Sibaya and surrounding areas. Submitted for Geology Hons. course, University of Natal, Durban.
REASONS FOR INCLUSION
1. Lake Sibaya contains the second largest population of hippopotamus (Hippopotamus amphibius) and crocodile(Crocodylus niloticus) in KwaZulu. It is the largest, natural freshwater lake in the country. The diversity of biota associated with the system is noted in section 10 & 11. The Lake is representative of flora and fauna in the coastal Lake Zone.
2. A freshwater goby (Silhouetta sibayi) is almost endemic to the system. Numerous other Red Data species occur in the system, their presence would be affected if the wetland was not preserved. The only known population of Vanilla roscheri (a climbing orchid) occurs on the Lake shore; the community would be threatened by destruction of the lake.
3. Lake Sibaya and environs has the capacity to support almost 250 hippo, hundreds of crocodile, other larger mammals presently extinct from the shores. The present natural area supports a wide diversity of flora and fauna with a range of habitats being incorporated in the area to allow for more variability and resilience. The wetland supports rural people of the region who, in many cases, are totally dependant on the water resource and associated flora and fauna.
4. Breeding population of hippopotamus (Hippopotamus amphibius), crocodile(Crocodylus niloticus), Fish Eagles (Haliaeetus vocifer), Reed and Whitebreasted Cormorant (Phalacrocorax africanus and P. carbo), Herons (Ardea spp.), Kingfishes (Halcyon sp.), Weavers and a variety of other waterbirds are found on the Lake. This wetland is an important link between Kosi Bay and St Lucia Bay, allowing for extension of tropical elements down the east coast.
5. Red Data species are noted in section 11. The whole lake is an important area for the endemic goby noted under 2. Water in the surrounding coastal plain often dries up completely during dry years, Lake Sibaya is then the only source of permanent water for birds and mammals.
6. Rhodes University established a research on the lake during the 1970's. Extensive investigations were carried out on the ecological features of the system with much valuable data being gathered. The area is used to illustrate sustained resource use and improved veld management. Biological studies are still underway, while outside organizations still apply to visit the area for research purposes. The establishment of a more formal conservation area around the lake will greatly assist educational programmes where field classes can be undertaken. Access for thousands of local people is easy; the range of habitats and species allows for more educational opportunities.
7. The lake and surrounding area is already being marketed for its tourist potential and has received favourable comments. The area is definitely scenic and has great recreation potential. When the Rhodes research station was in operation, the research opportunities attracted visiting scientists.
If you have any comments on this page, or need more information, please contact John Dini at nat_jd>@ozone.pwv.gov.za. This page is maintained by the South African Wetlands Conservation Programme and was last updated on 12 January 1999.