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  De Hoop Vlei
General information

 

Land uses
Ecology
Topography and geology
Hydrology and geohydrology
Climate
Threats
References
Useful links
Map

General information      Top

The lake is situated (34o26'S; 20o 22'E) on the coastal plain between 4m and 11m above the mean sea level.  It is 18 km long and 0,5 km wide with a surface area of 6.2 Km2 (750ha) when full. The depth of the lake is very variable from a maximum of 7 m during periods of flooding (only twice this century) to nearly completely dry (at least once this century) (Ref.2), causing the salinity to drop from 60ppt to 3ppt within a period of only 2 months (Ref.3). During occasions of extensive flooding, which has occurred only twice this century in 1906 and 1957 (Ref. 2), an area of up to 3000 ha on the plain southwest of De Hoop lagoon may be inundated to a depth of up to 3 m.

The closest town, Bredasdorp is 65 km from the Ramsar site.  The site is within the De Hoop Nature Reserve, which lies along the southern coast of the Western Cape Province .

The Sout River and its tributary the Potteberg River are the most important rivers feeding the De Hoop Vlei. There are also several fountains that discharge water into the northern part of the lagoon, which explains why this area never becomes as brackish as the rest of the lagoon.

The greater part of the Sout River catchment of De Hoop Vlei falls outside the reserve.

The statistics (Ref. 1) for the Sout River catchment is as follows:

  • Total surface area = 127 000 ha

  • Mean annual rainfall = 371 mm

  • Mean annual evaporation (MAE) = 1430 to 1470 mm

  • Mean annual runoff (MAR) to De Hoop Vlei = 17 mm or 21,9 million m3 (4,6% of rainfall)

  • Area under irrigation = 600 ha

Three wetland types are identified at De Hoop Vlei, namely:

  • Coastal freshwater lagoon

  • Coastal brackish lagoon

  • Seasonal freshwater marshes

Land uses        Top

The Ramsar site is part of the De Hoop Provincial Nature Reserve, owned by the state and managed by the Provincial Conservation Authorities. The terrestrial portion of the reserve covers an area of about 35 546 ha (355 km2) while the marine portion of the reserve covers an area of approximately 25 300 ha (253 km²).

Human activities are restricted to management activities associated with the reserve with a small amount of recreation in the form of game viewing, hiking, and mountain bikes.

Virtually the entire catchment of 127 000 ha, outside the reserve, is in private ownership and has been largely ploughed for establishment of wheatlands and pastures. The remaining privately owned land at the upper end of the lake consists largely of undeveloped rocky limestone hills which are used as rough grazing for sheep and cattle.
Natural:   The nature reserve has a high recreation potential, but the emphasis is on nature-orientated educational visits. Human activities are restricted to management activities associated with the reserve.  Frequent burning is the only veld management practice that is applied to this land.
Agricultural:  Virtually the entire catchment (127 000 ha) outside the reserve, is in private ownership and has been largely ploughed for establishment of wheatlands and pastures.  An area of 600 ha in the Sout River catchment is under irrigation.
Industrial:  

 

Urban:  The closest town, Bredasdorp is 65 km from the Ramsar site
Recreational:  A small amount of recreation in the form of game viewing, hiking, and mountain bikes is in taking place at the reserve. However, limited overnight accommodation and camping and picnic facilities are available at De Hoop as well as hiking trails. Facilities and numbers of visitors are limited to ensure that no damage is done to the prime conservation-worthy resources of the reserve. 

The provision of environmental education programmes receives high priority. An environmental education centre with accommodation for 60 persons has already been built on the eastern section of the reserve. Environmental education courses have been offered for groups of school children from 1985. At De Hoop an interpretative centre has been developed and walks and hikes will be offered in the near future.

There are proposals in the management plan to develop bird hides and a self-interpretative nature trail along the edge of the wetland. The possibility of zoning the wetland to cater for a limited amount of canoeing is also being looked at.

Ecology     Top

The boundary of the Ramsar site has been specified as the edge of the lagoon. Therefore the only broad habitat type occurring within the site is the aquatic habitat.

According to (Ref. 6) the vegetation of the surrounding area is Coastal Macchia on limestone substrate. Low and Rebelo (Ref. 7) classify this vegetation type as Limestone Fynbos.

Algae:  
Vegetation:  

Aquatic vegetation:   The margin of the lake is mostly bare and only a few Phragmites australis reedbeds are present, mainly around freshwater springs. The submerged macrophyte Potamogeton pectinatus forms extensive beds when suitable environmental conditions exist and may cover the greater part of the lake (Ref. 8).  This apparently contributes largely to the maintenance of the rich animal life in the vlei habitat (See under Birds).  Other submerged macrophytes include Ruppia and Chara species. Salicornia species are dominant on the exposed bed of the lagoon.  
Terrestrial Vegetation:  Acocks (Ref. 6) reported that two Veld Types, namely the Coastal Macchia on limestone and the Macchia are the predominant veld types of the surrounding reserve.  Very small areas of the Veld Types, Coastal Renosterveld and Knysna Forest , also occur at De Hoop Vlei.

According to the new vegetation classification for South Africa (Ref. 8) three major vegetation types are recognized in the surrounding reserve, viz. Limestone Fynbos, Mountain Fynbos, Dune Fynbos and Dune Thicket. Only very small areas of Laterite Fynbos, South and Southwest Coast Renosterveld and Afromontane (Knysna) Forest also occur. The greater part of area that is mapped as Dune Thicket in this area by Low and Rebelo (Ref. 8) is actually Dune Fynbos with smaller interspersed patches of Dune Thicket.  Melkhout thicket can also be regarded as a form of Dune Thicket. Sideroxylon inerme (White milkwood) trees are common along the lake.

The waterplant, Potamogeton pectinatus, contributes largely to the maintenance of the rich animal life in the vlei habitat and provides favourable habitats for other aquatic organisms such as zooplankton (Ref. 9 and 10) and abundant fish populations (Ref. 11).

Invertebrates:   The waterplant, Potamogeton pectinatus, contributes largely to the maintenance of the rich animal life in the vlei habitat and provides favourable habitats for other aquatic organisms such as zooplankton (Ref. 9 and 10)

Fish:  Only one indigenous fish species, Sandelia capensis has been recorded for De Hoop Vlei (Ref. 10), but it is possible that Galaxias zebratus also occurs in the lake. Oreochromis mossambicus has been introduced to the lake and now occurs in large numbers (Ref. 11 and 12).  Implementation of control measures to reduce the number of Oreochromis mossambicus, has been identified. It is possible to utilize this fish as a source of food for workers as part of the control programme.
Reptiles and AmphibiansThe Cape clawed frog (Xenopus laevis) is common (Ref. 8), but water turtles (Pelomedusa subrufa), which were present, in large numbers until the 1960's (Ref. 13) may have become a rarity (Ref. 14).

Birds:  To date 259 bird species, which represents 70% of the 369 species known in the south-western Cape , have been recorded in the De Hoop Nature Reserve (Ref. 8).   This high species richness is ascribed to the high habitat diversity in this area (Ref. 15).

At least 75 bird species, which are dependent on wetlands, have been recorded at De Hoop Vlei, including 12 of the 18 South African waterfowl species (Ref. 8). Regular monthly or quarterly counts of the birds on De Hoop Vlei have been undertaken since 1979 (Ref. 8).

Noteworthy numbers of birds recorded were recorded of the Yellow-billed Duck (Anas undulata) (Ref. 16), the Cape Shoveller (Anas smithii) (Ref. 17), the Redknobbed Coot (Fulica cristata) and the Egyptian Goose (Alopochen aegyptiacus).

Rare and threatened species that have been recorded are the White pelican (Pelecanus onocrotalus) (Ref. 19), the Little Bittern (Ixobrychus minutus) (Ref. 19), the Black Stork (Ciconia nigra) (Ref19), the Greater Flamingo (Phoenicopterus ruber) (Ref. 4), the Lesser Flamingo (Phoeniconaias minor), the Caspian Tern (Hydroprogne caspia) (Ref. 8) and the Chestnutbanded Sandplover (Charadrius pallidus) (Ref. 8).

De Hoop Vlei is thus an important foraging area for the White Pelican, which is regarded as rare in South Africa with only two breeding populations, namely on Dassen Island and Lake St. Lucia (Ref 17).

De Hoop Vlei is also an important moulting refuge for a number of waterfowl. The maximum of 1 216 Cape Shovellers which was recorded during a moulting migration during 1982 (Ref. 8) represents 6% of the estimated world population of this species (Ref. 17).

A notable event was the first reported large scale breeding attempt of the greater flamingo Phoenicopterus ruber in South Africa in this area in 1980 when up to 5000 birds were present and approximately 800 nests were built with a fledgling success of 35% (Ref. 4).

The surrounding De Hoop Nature Reserve is also an important refuge for a number of other threatened species including the southernmost breeding colony of Cape Vultures (Gyps coprotheres) in the Potberg Mountain and Damara Terns (Sterna balaenarum) and African Black Oystercatcher (Haematopus moquini) along the coast (Heÿl, 1983).
It is well known that this cosmopolitan waterplant (Potamogeton pectinatus) serves as a very important food resource to waterfowl in the family Anatidae (Ref. 1). It is possibly also the staple food of indigenous duck species such as the Yellowbilled Duck, which eats the bulbs, leaves and stolons (Ref. 20) and the red-knobbed coot which utilizes it extensively (Ref. 1). As such this plant, to a large extent, appears to determine the carrying capacity of the vlei for primary consumers such as coots and other waterfowl.

Mammals:  

Topography and geology      Top
Topography and geography:  In the northern boundary of the reserve, the land surface drops to the southwest in a series of four distinct terraces. These terraces, at elevations of 90 to 100m, 60m, 30 to 40m and 15 to 20m, are the result of marine transgressions. The Potberg is separated from the Dunes by a narrow valley part of which forms an area of endorheic drainage in a border depression. The Sout River has cut a deep gorge through the Dunes to discharge into the De Hoop coastal lake, which is separated from the sea by the Witsand dunefield. The limestone terrain exhibits typical karst topography. Solution and subsidence features include dolines, uvalas and poljes (circular and oval depressions) and cave systems. Many of these features follow the predominantly east-west orientation, which was established when the Dunes were laid down parallel to the old coastlines of the time of formation.
Geology: 

As the boundaries of the De Hoop Ramsar site is restricted to the high water mark of the coastal lake a description of the geology of the site would be pointless. The following is an account of the geology of the surrounding area, the De Hoop Nature Reserve.

The northern boundary of the reserve is characterized by the high-lying terrain of the Potberg range and the Hard Dunes (limestone hills) with a maximum height of 611 m and 224 m above sea level respectively. A hard calcrete capping less than 0,5 m thick generally occurs in the older limestone terrain with softer material below.

The Potberg represents the remnant of a syncline of the Cape Folded Ranges which is truncated to the south by a major fault at the base of the range. The Table Mountain Group (TMG) quartzite strata dip northwards forming steeper slopes and cliffs on the southern side (scarp slopes) and more gently dipping northerly slopes (dip slopes). Thick boulder talus and alluvial fans occur at the southern foot of the range. The TMG quartzites form sea cliffs where they are exposed beneath the Bredasdorp limestone.

The basement geology of the area comprises sedimentary rocks of the Table Mountain Group (quartzites), Bokkeveld Group (shales and mudstones) and Uitenhage Group (mainly shale conglomerates). The resistant quartzites of the TMG form the Potberg range while the softer shales and conglomerates have been planed by marine transgressions into a gently southward sloping series of terraces. To the north of the Reserve the Bokkeveld shales have been eroded into undulating hills. Remnants of the Tertiary (25 million year BP) "African I" erosion surface (peneplain) survive as isolated flat-topped hills capped by silcretes of the Grahamstown Formation.

The greater part of the reserve is underlain by Tertiary limestone of the Bredasdorp Formation. These limestones cover most of the Bokkeveld and Uitenhage basement rocks within the reserve. Exposed Bokkeveld Shales and only very small exposures of the red conglomerates of the Uitenhage Formation can be found in the eastern section of the reserve. The Bredasdorp limestones were deposited as shallow marine environments (the De Hoop lagoon formation with shell fossils) and as coastal dunes (most of the rest of the deposits). The oldest deposits (Wankoe Formation) form the higher lying Dunes into which the coastal plain had been eroded during subsequent marine transgressions. Subsequently new dune systems (Klein Brak and Waenhuiskrans Formations) were formed on the coastal plain. The most recent member of the Bredasdorp Group was deposited within the last 10 000 years as a strip of unconsolidated dunes along the coast (Strandveld Formation).

The sandstone and quartzite are approximately 4000 million years old and the limestone 5 million years.

Soils:  
  
Hydrology and geohydrology      Top

The site lies within a Winter Rainfall area. The lagoon is therefore at it's fullest during or just after winter. The water at this stage is relatively fresh, but gradually becomes brackish as it evaporates during the summer months.

Climate      Top

The Ramsar site is situated in the eastern part of the temperate winter rainfall region that has a Mediterranean climate

Precipitation:  

The mean annual rainfall is approximately 380 mm (De Hoop Nature Reserve Office) with the maximum mean monthly rainfall occurring in August and the minimum in December and January. Rainfall can however vary by 15 % - 17 % from one year to the next. Summer rains commonly occur as cloudbursts, but rainfall is predominantly cyclonic associated with eastward movement of low-pressure cells crossing the South-western and Southern Cape (Ref. 14 and Ref. 21. Orographic rainfall may account for large differences in rainfall between the lowlands and the high-lying ground such as the limestone hills and the Potberg, particularly towards the eastern extremity of the Potberg. Rainfall on the Dunes may exceed 400 mm and that on the Potberg may exceed 700 mm per year (1:250 000 isohyet value). The mean annual precipitation for the Sout River catchment is 369 mm (Ref. 21).

The wettest 3 months of the year is June, July & August (12% of MAP per month) while the driest 3 months of the year is December, January & February (4 to 5,5% of MAP per month). Rainfall is fairly evenly distributed over the year (7 to 12,5% of MAP per month) except for the 3 driest months (4 to 5,5% of MAP per month).

Precipitation in the form of mist occurs in autumn and winter. At times the whole Overberg area can be covered in a thick mist bank. 

Frost and hail occur occasionally

Temperature:  

The warm Agulhas current results in temperate winters and warm summers. Temperature averages 16,8C per annum with an average of 20,5C and average winter minimum of 13,2C (Ref. 21).  The warmest month is January with a mean air temperature of 22C. The coldest month is July with a mean air temperature of 11C.

Wind:

Windy conditions are common particularly in summer when the prevailing wind direction is south-westerly with an average velocity of 35 km/h. Wind speeds may reach 60km/h or more at times.

Threats      Top

The development and operation of the Overberg Test Range has not resulted in a significant disturbance to the bird life of De Hoop Vlei as the aircraft flights are kept well away from the lake. The possible impact of the missile testing range is being monitored and strict requirements have been laid down for the operation of the testing range to ensure that disturbance is kept to acceptable minimum levels.

The possibility that landuse practices in the catchment may threaten the lake due to eutrophication by fertiliser runoff, pesticides and siltation due to increased erosion should be investigated.

References   Top
Ref 1:  De Hoop Vlei South Africa . (1988). http://www.environment.gov.za/soer/nsoer/resource/wetland/de_hoop_ris.htm
Ref 2: BUTCHER, S.E. 1984. Environmental factors and the water regime of De Hoop Vlei. School of Environmental Studies Report no. 45, University of Cape Town .
Ref 3: COETZEE, D.J. 1983. Verslag oor die kuslyn tussen Arniston en Infanta. In Anon. The ecology of De Hoop Nature Reserve and environs/Die ekologie van De Hoop- natuurreservaat en omgewing. Vol. II. Unpublished report. Cape Dept. of Nature & Environmental Conservation, Environmental Impact Assessment Committee.
Ref 4: UYS, C.J., BROEKHUYSEN, G.J., MARTIN J. & MACLEOD, J.G.R.1963. Observations on breeding of the greater flamingo Phoenicopterus ruber Linnaeus in the Bredasdorp district, South Africa . The Ostrich 34: 129-154
Ref 5:  De Hoop Vlei http://www.environment.gov.za/Branches/BioConservation/17Ramsar/de_hoop/de_hoop_ris.htm
Ref 6:   ACOCKS, J.P.H. 1975. Veld Types of South Africa (2nd Ed). D.J.B. Killick (ed.). Memoirs of the Botanical Survey of South Africa . No. 40. 128 p.
Ref 7:   Low, A,B, and Rebelo, A.G. (eds) 1996. Vegetation of South Africa , Lesotho and Swaziland . Department of Environment Affairs and Tourism, Pretoria
Ref 8:     HEŸL, C.W. 1983. Voëllewe van die De Hoopse omgewing en die moontlike impak van ontwikkeling deur Krygkor. In Anon. The ecology of De Hoop Nature Reserve and environs/Die ekologie van De Hoop-natuurreservaat en omgewing. Vol. II. Unpubl. report. Cape Dept of Nature & Environmental Conservation, Environmental Impact Assessment Committee
Ref 9:  HARRISON , A.C. 1957. De Hoop Lake . Dept of Nature & Environmental Conservation Annual Rep. 14: 57-60
Ref 10:  SIEGFRIED, W.R. 1963. Observations on the reproduction and feeding of the Cape kurper Sandelia capensis (C. and V.) in De Hoop lake, Bredasdorp. Inves. Rep. 3. Cape Dept. Nat. Cons. 12 pp
Ref 11: VAN RENSBURG, K.J. 1966. Growth of Tilapia mosssambica (Peters) in the De Hoop Vlei and Seekoei Vlei. Dept of Nature Conservation Investl. Rep. 9. 7 pp
Ref 12: SCOTT, H.A. & HAMMAN, K.C.D. 1988. Recent fish records from De Hoop Vlei, a southern Cape coastal lake. Bontebok 6: 30-33.
Ref 13:  BRAND, D.J. 1961. A comparative study of the Cape Teal (Anas capensis Gmelin) and the Cape Shoveller (Spatula capensis Eyton) with special reference to breeding biology, development and food requirements. Ph.D. Thesis, Univ. S.A.
Ref 14: BUTCHER, S.E. 1984. Environmental factors and the water regime of De Hoop Vlei. School of Environmental Studies Report no. 45, University of Cape Town .
Ref 15: UYS, C.J. & MACLEOD, J.G.R. 1967. The birds of the De Hoopvlei Region, Bredasdorp, and the effect of the 1957 inundation over a 10 year period (1957-66) on the distribution of species. The Ostrich 38(4): 233-254.
Ref 16:  ROWAN, M.K. 1963. The Yellowbilled Duck Anas undulata Dubois in southern Africa . Ostrich, Suppl. 5
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