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172<br />
groundwater consumption in Natal/KwaZulu are provided in the chapter on the surface<br />
water resources <strong>of</strong> Natal/KwaZulu, elsewhere in this publication.<br />
Over 90% <strong>of</strong> South Africa's groundwater occurs in limited volumes in numerous small<br />
secondary aquifers, specifically in the near-surface fractured and weathered part <strong>of</strong> hard<br />
rock formations <strong>of</strong> igneous, metamorphic and sedimentary origin*. Secondary aquifers<br />
are used mainly on farms for domestic needs, for stock watering and for small scale<br />
irrigation. Villages and small to medium sized towns can also be supplied from suitable<br />
secondary aquifers. Larger volumes <strong>of</strong> groundwater are only found in a few geological<br />
formations with a relatively small areal distribution. These sources are the extensively<br />
leached (karstified) dolomitic strata <strong>of</strong> the southern and western Transvaal as well as the<br />
northern Cape; the (primary) geologically young coastal sand deposits, and alluvium along<br />
some rivers. The popular misconceptionthat all groundwater exists as "underground rivers<br />
and streams" is only true in a few dolomitic and limestone areas.<br />
Yields from boreholes in South Africa can be classified according to their potential use.<br />
Boreholes with a low yield « 1 t s-1) should be used for gardening as well as for domestic<br />
and stock purposes. Medium yield boreholes (1 - 5 t s-1) have a similar use, while high<br />
yield boreholes (5 - 20 t s-1) can supply small villages and towns. Very high yield<br />
boreholes (> 20 t s-1) are suitable for large scale irrigation and urban requirements. It<br />
should be borne in mind that in many parts <strong>of</strong> South Africa, typical borehole yields average<br />
less than 2 t s-1 (Vegter, 1984).<br />
The exploitation potential <strong>of</strong> groundwater is determined by the volume <strong>of</strong> water held<br />
underground, the recharge rate, and losses through seepage to springs, wetlands, streams,<br />
lakes, "estuaries", and the sea. Also important are evapotranspiration losses.<br />
Groundwater use is likewise constrained by practicality and economics. In secondary<br />
aquifers, low borehole yields effectively prevent exploitation <strong>of</strong>the resource for bulk water<br />
supplies. Umited demand and associated costs may also not justify the maximum<br />
exploitation <strong>of</strong> groundwater. In certain areas <strong>of</strong> the Karoo for example, groundwater<br />
*<br />
A useful glossary <strong>of</strong> South African groW'ldwater tenns can be foW'ld in the following: Parsons, R.,<br />
1995. A South African aquifer system management classification, WRC Report No. KV 77/95, Water<br />
Research Commission, Pretoria, 20 p. + app. Any comprehensive textbook on groundwater may<br />
likewise be consulted. See also: Pfannkuch, H-Q., 1990. 8sevier's Dictionary <strong>of</strong> Environmental<br />
Hydrogeology: in Enolish. French and Gennan, revised edition, 8sevier, Amsterdam, 332 p.