State of freshwater systems and resources in South Africa: #1
South Africa's hydrological regime is characterised by high variability, due to climatic conditions, and low water runoff, due to high absorption by soils (Walmsley 1991).
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Figure 3.7 indicates that South Africa has a mean annual precipitation (MAP) to mean annual runoff (MAR) ratio of 8.6%, that
is, only 8.6% of the rainfall is available as surface water. This is one of the lowest conversion ratios in the world.
Canada and Australia, which have similar MAP figures, have ratios of 65.7% and 9.8% respectively.
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Figure 3.7 Relationship between mean annual runoff and mean annual precipitation.
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The MAR for South Africa is estimated at 50 150 million m3 a-1. This is not distributed evenly throughout the country, with the Eastern seaboard having high runoff, whilst the western regions tend to have low runoff (Figure 3.8.)
Nor is it consistent over time, with great variability
between years (Figure 3.3 a-e).
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| Figure 3.8 Distribution of annual surface runoff.
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Of critical importance is
the relationship between groundwater and surface water. Groundwater
can only be abstracted on a sustainable basis at a rate less than,
or equal to, its long-term average recharge through infiltration of
rainwater. Already many of the streams that existed at the beginning
of the century have dried up due to over-extraction, and groundwater
failure is common in some of the more densely-populated areas
(Basson et al. 1997).
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| Figure 3.9 Groundwater harvest potential |
There are an estimated 50 000 new boreholes drilled in South
Africa per year by the private sector, but the majority are dry or
low yielding (E Braune,DWAF, pers. comm.). Figure 3.10
shows the growth in number of boreholes registered on the
National Groundwater Database. The present figure (1999) is 197 811
extant boreholes. |
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Figure 3.10 Total number of boreholes
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Wetlands are some of the most threatened
aquatic habitats in South Africa (Walmsley 1991)
. Threats to wetlands
include human development activities, channelisation, drainage, crop
production, effluent disposal and water abstraction; that is, most
human-induced land-use changes (see Terrestrial Ecosystem section). Begg (1986) states that
"wetlands formerly occupied between 10 and 15% of
every catchment in Natal. |
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| A wetland in South Africa |
Within the last fifty years
wetlands in these same areas have been reduced to a few
scattered remnants, and in certain catchments virtually
eliminated". This probably applies to the rest of
South Africa, but little information is available about
the extent of previously-existing wetland areas. |
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Even the present DEA&T database on wetlands is limited to 1
377 wetlands as shown in Figure 3.11. Of these, 21% are
marine and estuarine, 21% are endorheic pans, 15% are
riverine, 5% are lacustrine, 19% are
palustrine, and 18% are man-made (Cowan and Van Riet 1998).
Of the 829 naturally-occurring freshwater wetlands, 13.5% have full
protection within a national park, provincial nature reserve or
wildlife sanctuary and 3.9% are partly protected (Cowan and Van Riet
1998). |
| Figure 3.11 Distribution of wetlands in South Africa |
South Africa currently has 16 wetlands designated as wetlands of
international importance in accordance with the Ramsar Convention. They are De Hoop
Vlei, Barberspan, De Mond State Forest/Heuningnes
Estuary, Blesbokspruit, Turtle Beaches/Coral Reefs of
Tongaland, St Lucia System, Langebaan, Wilderness Lakes,
Verlorenvlei, Orange River Mouth, Kosi Bay system, Lake
Sibaya, Natal Drakensberg Park, Ndumo Game Reserve;
Seekoeivlei (see Cowan and Marneweck 1996) and Nylsvlei
Figure 3.11.Of
these, only six are inland, freshwater wetlands.
The present status of estuarine environments is dealt with in
the Marine and Coastal section of this report. However, one of the important
aspects of the estuarine environment is the amount of freshwater
entering the system. River flow through an estuary maintains the
salt balance in the estuary and ensures that the estuary mouth
remains open.
The environmental water requirements of estuaries as estimated by
DWAF (1986) are given in Table 3.3. Where available,
data are presented on the present flow through the estuary mouth.
The percentage of MAR flowing through the estuary varies
considerably for each river, because of aspects such as
climatic variability, level of development, land use and
river regulation.
Major river |
Virgin MAR of catchment (million
m3 a-1)
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Total estuarine area (ha)
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Evaporative requirement (million
m3 a-1)
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Flooding requirement (million
m3 a-1)
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Total requirement (million m3
a-1)
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Mean present flow (million m3
a-1)
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Present flow as % of virgin MAR
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Vaal/ Orange
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11 244
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534,06
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534,06 |
6783,42 (1995-1997)
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60%*
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Olifants |
1008 |
648 |
9,17 |
66,38 |
75,55 |
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Great Berg
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913
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6085
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58,08 |
69,07 |
127,15 |
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Breede |
1873 |
1472 |
11,84 |
136,78 |
148,62 |
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Gouritz |
662 |
188 |
1,80 |
37,73 |
39,53 |
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| Gamtoos
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495 |
175 |
1,76 |
35,04 |
36,80 |
78,16 (1968-1970) |
16% |
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Swartkops
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100 |
1163 |
12,65 |
6,35 |
18,99 |
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Sundays
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280 |
268 |
3,01 |
14,28 |
17,29 |
169,81 (1994-1996)
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61%**
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Bushmans
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95 |
1416 |
12,52 |
7,34 |
19,86 |
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Great Fish
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519 |
199 |
1,67 |
36,82 |
38,49 |
740,04 (1996 only)
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143%
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Buffalo |
320 |
861 |
5,41 |
21,48 |
26,88 |
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Great Kei
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1043 |
298 |
1,59 |
74,48 |
76,07 |
417,95 (1994-1996)
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40%
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| Mzimkulu
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1382
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184 |
0,68 |
84,76 |
85,44 |
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| Mgeni |
740 |
449 |
1,90 |
154,30 |
156,20 |
294,63 (1992-1994) |
40%
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Tugela |
3865 |
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230,00
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230,00 |
2837,20 (1994-1996)
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73%
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Mfolozi
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972 |
39345 |
256,65 |
149,76 |
406,41 |
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* Expected to reduce because of the Lesotho Highlands Water
Development Scheme
** Augmented from the Fish River. |
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There is also information about Freshwater Systems and Resources in the following reports:
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Metropolitan reports:
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Affairs and Tourism. All Rights Reserved.
Site maintained by the Directorate Environmental Information and Reporting
Last update: October 1999
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