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Grimsditsch et al Pemba Resilience Survey 2009 low res

Grimsditsch et al Pemba Resilience Survey 2009 low res.pdf

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D<strong>et</strong>ailed Results<br />

Over<strong>al</strong>l site <strong>res</strong>ilience rankings<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

Anthropogenic<br />

Connectivity<br />

Fish groups<br />

Cor<strong>al</strong> associates<br />

Cor<strong>al</strong> Population<br />

Cor<strong>al</strong> Condition<br />

Shade & screen<br />

5<br />

0<br />

Mis<strong>al</strong>i<br />

Mandela<br />

Manta<br />

Njao Gap<br />

Simba<br />

Kokota<br />

Swiss<br />

Fundo Inner<br />

The Hole<br />

Msuka Bay<br />

Fundo Lagoon<br />

Fundo Outer<br />

Paradise<br />

Extremes &<br />

Acclimatization<br />

Cooling &flushing<br />

Benthic<br />

Mis<strong>al</strong>i ranked highest of the sites, fol<strong>low</strong>ed by Mandela and Manta. Paradise and Fundo Outer ranked <strong>low</strong>est.<br />

These <strong>res</strong>ults cor<strong>res</strong>pond well with hard cor<strong>al</strong> cover (highest at Mis<strong>al</strong>i, Mandela and Manta but <strong>low</strong>est at<br />

Paradise and Fundo Outer). As we sh<strong>al</strong>l see, the differences in <strong>res</strong>ilience factors b<strong>et</strong>ween he<strong>al</strong>thy and<br />

degraded sites are mostly driven by factors relating to cor<strong>al</strong> population (recruitment, fragmentation, dominant<br />

size classes and largest cor<strong>al</strong>s) and cor<strong>al</strong> associates (branching <strong>res</strong>idents, obligate feeders, comp<strong>et</strong>itors,<br />

bioeroders and cor<strong>al</strong>livo<strong>res</strong>).<br />

Cor<strong>al</strong> Population<br />

Standard deviation of <strong>res</strong>ilience factors<br />

Cor<strong>al</strong> associates<br />

Cooling &flushing<br />

Benthic<br />

Extremes & Acclimatization<br />

Fish groups<br />

Cor<strong>al</strong> Condition<br />

Shade & screen<br />

Anthropogenic<br />

Connectivity<br />

0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1<br />

Standard deviation of <strong>res</strong>ilience indicators b<strong>et</strong>ween sites shows that the largest variations are caused by<br />

factors related to cor<strong>al</strong> population and cor<strong>al</strong> associates b<strong>et</strong>ween degraded and he<strong>al</strong>thier sites. Very little<br />

variation was found in connectivity b<strong>et</strong>ween sites, as they are influenced by similar prevailing currents and<br />

there is little evidence to identify larv<strong>al</strong> sources. Anthropogenic influences <strong>al</strong>so did not vary greatly b<strong>et</strong>ween<br />

sites- most sites are heavily fished or influenced by overspill effects of overfishing in neighbouring sites, while<br />

there is little over<strong>al</strong>l effect from land-based pollution or nutrients.<br />

32

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