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View/Open - University of Zululand Institutional Repository

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183<br />

good. with a total dissolved solids or salts (TDSI* content <strong>of</strong> up to about 500 mg r 1 ,<br />

which is much the same as the surface water in the river channel. For their continued<br />

satisfactory performance, well points generally need to be back-washed every 6 - 12<br />

months. The installation <strong>of</strong> shallow well points in river beds was frequently resorted to<br />

as an emergency source <strong>of</strong> water, when many <strong>of</strong> the rivers in NatallKwaZulu virtually dried<br />

up during the severe drought years <strong>of</strong> 1982/83 and again in 1992/93. Shallow well point<br />

systems currently serve as a source <strong>of</strong> domestic and industrial water on the Buffalo and<br />

Nondweni rivers in the interior <strong>of</strong> the province, and on the Matigulu, Nonoti, Mdloti, Lovu,<br />

Mpambanyoni, Mtwalume and Imbizana rivers in the coastal zone.<br />

• Deep screen wells<br />

Deep screen wells have been installed in several <strong>of</strong> the upper estuarine reaches <strong>of</strong> rivers<br />

in NatallKwaZulu, where alluvial and estuarine sediment depth is considerable. The depth<br />

<strong>of</strong> screen wells, from which water is obtained by means <strong>of</strong> a pump situated in a sump<br />

beneath the screen, varies in the approximate range <strong>of</strong> 15 - 30 m. Potential screen well<br />

sites must be subjected to a preliminary test boring investigation, in order to ensure the<br />

accurate location <strong>of</strong> the screen in the sandy aquifer - given that impermeable silt and clay<br />

horizons are frequently also present - and to optimize screen opening size in terms <strong>of</strong> the<br />

particle size distribution <strong>of</strong> the sand. Yields from (20 - 25 m deep), 200 - 300 mm<br />

diameter screen wells vary in the range <strong>of</strong> 60 - 180 m 3 h- 1 . Groundwater from screen<br />

wells generally has a higher iron content (due to the chemically reducing conditions<br />

prevailing atthe abstraction depth in the aquifer), than is the case for groundwater derived<br />

from shallower depths down to about 5 - 6 m. An iron content <strong>of</strong> up to about 40 mg r 1<br />

is frequently encountered in the deeper groundwater. The iron is readily removed by<br />

aeration and storage. If located too close to the shoreline <strong>of</strong> the "estuary" (within a<br />

distance <strong>of</strong> about 2 km therefroml, the chloride content <strong>of</strong> the deeper groundwater is <strong>of</strong>ten<br />

somewhat marked. If screen wells are sited within a distance <strong>of</strong> about 1 km from the<br />

shoreline, sea water intrusion becomes a possibility with continuous long term extraction.<br />

Generally, the quality <strong>of</strong> the groundwater obtained from deep screen wells in alluvial and<br />

estuarine sediments is good to moderate, with TDS values usually in the range <strong>of</strong><br />

400 - 1 200 mg r'. Deep screen wells have been installed as a source <strong>of</strong> urban<br />

*<br />

The terms "total dissolved solids" and "total dissolved salts" are both used in the scientific literature.

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