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Okavango Delta Management Plan - Ramsar Convention on Wetlands

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Subsequently, flow from the Thamalakane passes through a break in the fault downstream<br />

of Maun into the Boteti River. There is a potential drainage route downstream to the<br />

Makgadikgadi Pans, and into the Nhabe River and downstream to Lake Ngami, though this<br />

has not been observed since 1989. Since 2000, the Boteti has at best reached Chanoga,<br />

which is approximately 60 km downstream. The Boteti River downstream and its eventual<br />

outfall to the Makgadikgadi Pans are excluded from the area of the river basin, and from<br />

the <str<strong>on</strong>g>Ramsar</str<strong>on</strong>g> wetland area.<br />

2.2.6.4 Flooding pattern<br />

Sediment depositi<strong>on</strong>, and swamp vegetati<strong>on</strong> with associated peat aggradati<strong>on</strong> raise the<br />

channels above the flood plains. The transfer of flow between the river and flood plains is<br />

highly dynamic depending <strong>on</strong> the period of the flood from upstream, antecedent ground<br />

water c<strong>on</strong>diti<strong>on</strong>s and the rainfall over the <str<strong>on</strong>g>Delta</str<strong>on</strong>g>.<br />

This causes extreme spatial and temporal variati<strong>on</strong>s in the flooding pattern, which change<br />

over at least four time scales. The l<strong>on</strong>gest is over geological periods of 10 000 to 1 000 000<br />

years and at times the <str<strong>on</strong>g>Delta</str<strong>on</strong>g> has probably been a completely dry desert with sand dunes,<br />

while at other times it has been completely flooded. Since around 1850 the flooding pattern<br />

has moved from a very westerly to a central and now a very easterly distributi<strong>on</strong> (McCarthy<br />

and Ellery, 1998), with some recent evidence of a return to a westerly trend. There are dry<br />

and wet periods as well with about 8 and 18 years interval (Tys<strong>on</strong> et al., 2002), which<br />

causes the seas<strong>on</strong>ally flooded areas to withdraw and expand. Finally the flooding pattern<br />

can change from year to year caused by local factors such as vegetati<strong>on</strong> blockages in the<br />

streams causing damming and overflow of riverbanks. This large variati<strong>on</strong> in flooding<br />

pattern is <strong>on</strong>e of the important and unique features of the <str<strong>on</strong>g>Okavango</str<strong>on</strong>g> <str<strong>on</strong>g>Delta</str<strong>on</strong>g>.<br />

2.2.6.5 Infiltrati<strong>on</strong><br />

The calculati<strong>on</strong> of the water balance within the <str<strong>on</strong>g>Delta</str<strong>on</strong>g> reveals that the infiltrati<strong>on</strong> to<br />

groundwater is very large. In <strong>on</strong>e floodplain system it amounted to 90% of the total inflow.<br />

Groundwater levels that were 3–5 meters below ground rose with arrival of the water within<br />

a few days up to the surface. As far away as 600 meters from the floodplain groundwater<br />

levels rose 1.5 m<strong>on</strong>th after arrival of the flood. This was caused by lateral groundwater flow,<br />

which became the dominant infiltrati<strong>on</strong> process after the first days and transferred at least<br />

80% of the total infiltrati<strong>on</strong> to the surroundings. The impact area was calculated to be 3–6<br />

times larger than the floodplain itself. This surrounding area of riverine woodland is a<br />

dominant element of the vegetati<strong>on</strong> throughout the <str<strong>on</strong>g>Delta</str<strong>on</strong>g>. It is probably str<strong>on</strong>gly dependent<br />

<strong>on</strong> this mechanism of flooding – infiltrati<strong>on</strong> – lateral flow. The lateral flow itself is in all<br />

likelihood driven by transpirati<strong>on</strong> from the riverine woodland. Early hydrological models<br />

(Gieske, 1997, Dincer et al., 1987) neglected the groundwater-surface water interacti<strong>on</strong>.<br />

The new generati<strong>on</strong> of models (Bauer et al., 2006, ODMP Mike SHE model) take this<br />

process into account. It is a dominant hydrological process, which has large implicati<strong>on</strong>s<br />

for the understanding of the <str<strong>on</strong>g>Delta</str<strong>on</strong>g> ecology. For instance the proposed water development<br />

projects like clearing of channels in the <str<strong>on</strong>g>Delta</str<strong>on</strong>g> of vegetati<strong>on</strong>, upstream water diversi<strong>on</strong>s and<br />

building of dams, are all acti<strong>on</strong>s that will reduce the durati<strong>on</strong> of the seas<strong>on</strong>al flooding and<br />

its spatial extent. The impacts will not be restricted to the floodplains but affect large areas<br />

of woodland as well.<br />

2.2.6.6 Island growth and salinity<br />

In the <str<strong>on</strong>g>Okavango</str<strong>on</strong>g> <str<strong>on</strong>g>Delta</str<strong>on</strong>g> about 94% of inflowing solutes are retained within the <str<strong>on</strong>g>Delta</str<strong>on</strong>g> (Table<br />

2-1). This could lead to an entirely saline envir<strong>on</strong>ment, but that is not the case: the surface<br />

waters have very low salinity with a freshwater biota. It has been deduced that the<br />

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