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the role of tourism in natural resource management in the okavango ...

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<strong>the</strong> wildlife populations and <strong>the</strong>ir utilisation (Thakadu, 1997; DWNP, 1999; Mbaiwa,<br />

1999; Mbaiwa, 2004). W<strong>in</strong>er (1995) states that CBNRM projects <strong>in</strong> WMAs seek, as a<br />

pr<strong>in</strong>cipal aim, to return custodianship <strong>of</strong> <strong>natural</strong> <strong>resource</strong>s to <strong>the</strong> local communities <strong>in</strong><br />

order for conservation to be l<strong>in</strong>ked to rural production systems that generate wealth,<br />

ra<strong>the</strong>r than conservation be<strong>in</strong>g viewed as be<strong>in</strong>g <strong>in</strong> conflict with such rural production<br />

systems, as has <strong>of</strong>ten been <strong>the</strong> case.<br />

WMAs are fur<strong>the</strong>r sub-divided <strong>in</strong>to Controlled Hunt<strong>in</strong>g Areas (CHAs). CHAs form<br />

smaller <strong>management</strong> units with<strong>in</strong> WMAs, which become <strong>the</strong> 'unit <strong>of</strong> production'<br />

(Rozemeijer and van der Jagt, 2000; Mbaiwa, 2002). Therefore, CHAs are<br />

adm<strong>in</strong>istrative blocks used by <strong>the</strong> Department <strong>of</strong> Wildlife and National Parks to<br />

allocate wildlife quotas, and Botswana is divided <strong>in</strong>to 163 CHAs, which are zoned for<br />

various types <strong>of</strong> wildlife utilisation (both consumptive and non-consumptive uses),<br />

under commercial or community <strong>management</strong>. In communal areas, CHAs are zoned<br />

around exist<strong>in</strong>g settlements and those under community <strong>management</strong> are designed<br />

to benefit <strong>the</strong> local people (Rozemeijer and van der Jagt, 2000; Mbaiwa, 2002;<br />

Mbaiwa, 2004).<br />

Wildlife Management Areas (WMAs) <strong>in</strong> <strong>the</strong> Okavango region are sub-divided <strong>in</strong>to 49<br />

CHAs. By 2001, a total <strong>of</strong> 12 CHAs were allocated to different communities <strong>in</strong> <strong>the</strong><br />

Okavango for <strong>tourism</strong> purposes, and 15 CHAs were leased to safari companies by<br />

<strong>the</strong> Tawana Land Board for both hunt<strong>in</strong>g and photographic purposes. The rest <strong>of</strong> <strong>the</strong><br />

CHAs are used for multipurpose activities and are under <strong>the</strong> control <strong>of</strong> <strong>the</strong> Tawana<br />

Land Board (Mbaiwa, 2004).<br />

Even though wildlife and related <strong>tourism</strong> policies <strong>in</strong> Botswana give part <strong>of</strong> <strong>the</strong><br />

responsibility for manag<strong>in</strong>g and adm<strong>in</strong>ister<strong>in</strong>g wildlife <strong>resource</strong>s to local<br />

communities, <strong>the</strong>y fail to def<strong>in</strong>e <strong>the</strong> objective <strong>of</strong> government <strong>in</strong> relation to CBNRM,<br />

nor do <strong>the</strong>y provide firm guidance for its implementation (Rozemeijer and van der<br />

Jagt, 2000). Mbaiwa (2002; 2004) also notes that although local people are given<br />

partial rights to manage land and wildlife <strong>resource</strong>s <strong>in</strong> <strong>the</strong> Okavango Delta, much <strong>of</strong><br />

it rema<strong>in</strong>s centralised as land is only leased to <strong>the</strong>m for a 15 year period and wildlife<br />

<strong>resource</strong>s rema<strong>in</strong> wholly <strong>the</strong> property <strong>of</strong> <strong>the</strong> government, except for <strong>the</strong> quota<br />

allocated to <strong>the</strong> community. Cassidy (2001) states that <strong>the</strong>re is very little <strong>natural</strong><br />

<strong>resource</strong> monitor<strong>in</strong>g be<strong>in</strong>g undertaken, and few <strong>management</strong> decisions made, by<br />

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