Home Wetlands in South Africa Ramsar Sites Definition of a Wetland
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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 |
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The
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The
statistics (Ref. 1) for the
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Three
wetland types are identified at De Hoop Vlei, namely:
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| Land uses Top | ||||||
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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). |
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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. |
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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. |
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| Natural:
The
nature reserve has a high recreation potential, but the emphasis is on
nature-orientated educational visits. |
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| 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 |
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| Industrial:
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| 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. 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. |
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| Ecology Top | ||||||
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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. |
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| Algae: | ||||||
| Vegetation:
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| 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 |
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| 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 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) 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). |
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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) |
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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. |
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Reptiles
and Amphibians: The
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). |
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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). |
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Noteworthy
numbers of birds recorded were recorded of the Yellow-billed Duck (Anas
undulata) (Ref. 16), the 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 |
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A
notable event was the first reported large scale breeding attempt of
the greater flamingo Phoenicopterus ruber in |
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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. |
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Mammals: |
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| 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 |
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| 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 |
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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. |
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| Soils:
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| Hydrology and geohydrology Top | |||||
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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. |
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| Climate Top | |||||
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The Ramsar site is situated in the eastern part of the temperate winter rainfall region that has a Mediterranean climate | ||||
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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
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. |
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| Threats Top | |||||
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The
development and operation of the |
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| References Top | |||||
| Ref 1:
De
Hoop Vlei South |
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| Ref 2: BUTCHER,
S.E. 1984. Environmental factors and the water regime of De Hoop Vlei.
School of Environmental Studies Report no. 45, |
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| 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. |
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| 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, |
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| Ref
5:
De
Hoop Vlei http://www.environment.gov.za/Branches/BioConservation/17Ramsar/de_hoop/de_hoop_ris.htm |
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| Ref
6:
ACOCKS, J.P.H. 1975.
Veld Types of |
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| Ref
7: Low,
A,B, and Rebelo, A.G. (eds) 1996. Vegetation of |
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| 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. |
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| Ref
9: |
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| Ref
10: SIEGFRIED,
W.R. 1963. Observations on the reproduction and feeding of the |
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| 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 |
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| Ref
13: BRAND,
D.J. 1961. A comparative study of the |
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| Ref
14: BUTCHER,
S.E. 1984. Environmental factors and the water regime of De Hoop Vlei.
School of Environmental Studies Report no. 45, |
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| 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. |
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| Ref
16: ROWAN,
M.K. 1963. The Yellowbilled Duck Anas undulata Dubois in
southern |
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