Okavango Delta Management Plan - Ramsar Convention on Wetlands
Okavango Delta Management Plan - Ramsar Convention on Wetlands
Okavango Delta Management Plan - Ramsar Convention on Wetlands
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ecause surface head fires cause least damage to the grass sward and crown fires can cause<br />
maximum damage to woody vegetati<strong>on</strong> when fire is used to c<strong>on</strong>trol bush encroachment;<br />
ii. When burning to remove moribund and/or unacceptable grass material a cool fire of 2 000 kJ/s/m is necessary. This can be achieved when the grass fuel load is >4 000 kg/ha,<br />
the air temperature is >25°C and the relative humidity 13 mm. When burning to c<strong>on</strong>trol the<br />
encroachment of undesirable plants like bush encroachment, a high intensity fire is required and it is<br />
recommended that this be applied before the first spring rains in August/September when it is<br />
extremely hot and dry.<br />
iv. In the case of burning in the Seas<strong>on</strong>al Swamps where the growth of the vegetati<strong>on</strong> is generally<br />
influenced by the annual flood waters entering the <str<strong>on</strong>g>Delta</str<strong>on</strong>g> the ideal burning window for removing<br />
moribund and/or unpalatable grass material is during the period May to July, applying the fires<br />
when the grass sward is dormant before the flood waters start rising.<br />
v. If it should be necessary to reduce the growth of trees and shrubs in the Seas<strong>on</strong>al Swamps then<br />
burning must be applied later in the winter during August/September when it is extremely hot and<br />
dry thereby ensuring high intensity fires necessary to c<strong>on</strong>trol encroaching trees and shrubs.<br />
vi. When burning to remove moribund and/or unacceptable grass material the frequency of burning<br />
will depend up<strong>on</strong> the accumulati<strong>on</strong> rate of excess grass litter. Field experience indicates that<br />
burning is necessary for this reas<strong>on</strong> when the grass fuel load exceeds 4 000 kg/ha and therefore the<br />
frequency of burning of areas in the Seas<strong>on</strong>al Swamps and the Acacia, Burkea and Mopane<br />
Woodlands can be determined using this criteri<strong>on</strong>.<br />
vii. In order to prevent overgrazing it is important to ensure that the burnt area exceeds the short term<br />
forage requirements of the grazing animals that are attracted to the highly palatable and nutritious<br />
re-growth that develops after a burn i.e. burn relatively large areas at any <strong>on</strong>e time. Another<br />
effective strategy is to apply a series of patch burns at regular intervals throughout the durati<strong>on</strong> of<br />
the burning window during the dormant seas<strong>on</strong>. This has the effect of attracting the grazing animals<br />
to the newly burnt areas after the different fires thereby spreading the impact of grazing over the<br />
entire burnt area and avoiding the detrimental effects of heavy c<strong>on</strong>tinuous grazing after the burns.<br />
5.2.7.2 Practical Applicati<strong>on</strong> of C<strong>on</strong>trolled Burning<br />
In the practical applicati<strong>on</strong>, a c<strong>on</strong>trolled burning program should be guided by the<br />
following factors (ODMP – Fire <str<strong>on</strong>g>Management</str<strong>on</strong>g> <str<strong>on</strong>g>Plan</str<strong>on</strong>g>, 2006):<br />
a) The weather c<strong>on</strong>diti<strong>on</strong>s as described and assessed using the recommended Fire<br />
Danger Rating System should be appropriate for burning.<br />
b) Appropriate burning procedures for the applicati<strong>on</strong> of the c<strong>on</strong>trolled burn<br />
should be used i.e. applying a block burn or a patch mosaic burn<br />
c) Adequate and appropriate firebreaks for the area being burnt should be<br />
provided or be in place.<br />
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