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<strong>and</strong> nutrient-depleted. In contrast, water released from near the bot<strong>to</strong>m is usually cold, oxygen-depleted,<br />

<strong>and</strong> nutrient-rich that is <strong>of</strong>ten high in hydrogen sulfide, iron <strong>and</strong>/or manganese. These differences in water<br />

quality can have significant impacts on downstream flora <strong>and</strong> fauna.<br />

Eutrophication <strong>of</strong> reservoirs may occur as a consequence <strong>of</strong> large influxes <strong>of</strong> organic material <strong>and</strong>/or<br />

nutrients. In many cases these are the consequence <strong>of</strong> human activities in the catchment. Eutrophication can<br />

result in blooms <strong>of</strong> blue-green algae (Figure 2.3) which as well as being aesthetically unpleasant are, in some<br />

instances, <strong>to</strong>xic <strong>and</strong> can cause oxygen depletion at the bot<strong>to</strong>m <strong>of</strong> the reservoir <strong>and</strong> increased pH <strong>and</strong> oxygen<br />

in the surface waters.<br />

2.5 Impacts on sediment<br />

10<br />

Figure 2.3. Algal bloom in the Hartebespoort Reservoir in South Africa.<br />

Reservoirs reduce flow velocity <strong>and</strong> so enhance sedimentation. Consequently, over time they fill with sediment.<br />

The rate at which a reservoir fills depends on characteristics <strong>of</strong> the catchment in which the <strong>dam</strong> is located,<br />

human l<strong>and</strong>-use practices <strong>and</strong> the operation <strong>of</strong> the <strong>dam</strong>. The reduction in sediment in rivers downstream <strong>of</strong><br />

<strong>dam</strong>s can result in increased erosion <strong>of</strong> river banks <strong>and</strong> beds, loss <strong>of</strong> floodplains <strong>and</strong> degradation <strong>of</strong> coastal<br />

deltas. In some circumstances increased sedimentation (aggradation) occurs because material entering from<br />

tributaries cannot be moved by the regulated flows.<br />

The Lower Nile River has been affected by the construction <strong>of</strong> two <strong>dam</strong>s. The Aswan (1902) <strong>and</strong> the<br />

Aswan High (1970) <strong>dam</strong>s were built <strong>to</strong> control the floodwaters <strong>of</strong> the Nile, <strong>to</strong> generate electricity <strong>and</strong> <strong>to</strong><br />

provide year-round irrigation. These <strong>dam</strong>s have significantly increased the amount <strong>of</strong> l<strong>and</strong> available for<br />

agriculture <strong>and</strong> lengthened the agricultural year. Other changes, however, have been less favorable. The<br />

Aswan High Dam traps more than 98% <strong>of</strong> the sediment transported by the Nile, reducing the deposition <strong>of</strong><br />

nutrient-rich silts on<strong>to</strong> downstream floodplains <strong>and</strong> the delta (Stanley <strong>and</strong> Warne 1998). Offshore fisheries<br />

that depended on nutrients from the Nile have drastically declined (Nixon 2004). The delta constitutes<br />

two-thirds <strong>of</strong> Egypt’s arable l<strong>and</strong>, but because it is being starved <strong>of</strong> fluvial sediments, it is steadily yielding <strong>to</strong><br />

coastal erosion at a rate <strong>of</strong> around 5-8 m per year (Stanley <strong>and</strong> Warne 1998). In addition, reduced soil fertility<br />

means that farmers have <strong>to</strong> apply increasing amounts <strong>of</strong> fertilizer <strong>to</strong> replace the nutrient-rich sediments<br />

trapped in the reservoir.<br />

Source: Matthew McCartney

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