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Cesar2000-Economics of Coral Reefs.pdf

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Table 3.<br />

Tied P-Values for Differences in Perceived Trends between Resource, Habitats, Threats and Compliance Categories.<br />

Non-Parametric Test Statistic<br />

Indicators _________________________________________________________<br />

CpUE Habitats Threats Compliance<br />

Test for Variation Between Indicator<br />

Categories (Kruskal-Wallis) 1 0.09 0.0001 0.0001 0.0001<br />

1<br />

Siegel & Castellan (1988).<br />

Indicator categories reflect broad groupings <strong>of</strong> resources, habitats, threats or management rules (e.g., ‘finfish’ and ‘shellfish’ resources for the CpUE<br />

indicator).<br />

P-values show the significance <strong>of</strong> the test statistic. A p-value <strong>of</strong> 0.0001 indicates a probability <strong>of</strong> less than one in 10,000 that the differences in<br />

perceptions for the various categories occurs by chance (SAS 1998).<br />

The Kruskal-Wallis test is a non-parametric version <strong>of</strong> a one-way analysis <strong>of</strong> variance by ranks that tests the null hypothesis that the categories<br />

come from the same distribution.<br />

No. <strong>of</strong> responses<br />

180<br />

160<br />

140<br />

120<br />

100<br />

80<br />

60<br />

40<br />

20<br />

0<br />

Declining<br />

a lot<br />

Catch per unit <strong>of</strong> effort perceptions<br />

Declining<br />

a little<br />

Stable<br />

N: 399 reponses (3 resources per focus group)<br />

Improving<br />

a little<br />

Improving<br />

a lot<br />

Figure 2. Distribution <strong>of</strong> perceptions on trends in the<br />

catch per unit <strong>of</strong> effort <strong>of</strong> key resources.<br />

3. RESULTS<br />

3.1 Perceived Trends in<br />

Catch-per-unit-<strong>of</strong>-effort (CpUE)<br />

Community groups were generally pessimistic about resource<br />

trends. Out <strong>of</strong> 399 responses, only 39 (10 percent)<br />

perceived an improving CpUE over the last decade<br />

(figure 2). Moreover, only 11 responses at 6 sites (3<br />

percent) indicated a positive trend that was related to<br />

coastal resource management. Where this occurred,<br />

communities identified prevention <strong>of</strong> destructive fishing,<br />

creation <strong>of</strong> sanctuaries, controls in harvesting <strong>of</strong><br />

particular species, and a ban on external fishermen as<br />

causing the improvement in CpUE. Declining CpUE,<br />

by contrast, was thought to be caused by overfishing<br />

(the most frequent answer) destructive fishing practices,<br />

cyclones, increased population, the use <strong>of</strong> nets and night<br />

diving, siltation, water pollution, coral destruction, the<br />

construction <strong>of</strong> causeways 4 , and habitat degradation.<br />

Differences in CpUE perceptions between resource<br />

categories were only significant at the 10 percent level<br />

(table 3). Pairwise comparisons indicated that the CpUE<br />

for bêche-de-mer (Holothuriae) was perceived as having<br />

declined faster than for shellfish, clams, reef finfish and<br />

octopus, but this result was only significant at the 10<br />

percent level 5 .<br />

3.2 Perceived Trends in Coastal Habitats<br />

Only a minority <strong>of</strong> 396 responses (22 percent) shared<br />

the perception that the quality <strong>of</strong> coastal habitats had<br />

improved. Most (52 percent) mentioned a decline (figure<br />

3). The reasons <strong>of</strong>fered for mangrove and seagrass<br />

improvements were generally unrelated to coastal management.<br />

By contrast, the majority <strong>of</strong> the reasons given<br />

4<br />

Causeways are raised roads built over bodies <strong>of</strong> water which link, for<br />

example, the surface <strong>of</strong> atoll islets.<br />

5<br />

This was tested using a Mann-Whitney rank test (Siegel & Castellan<br />

1988).<br />

174<br />

JEFF MULLER, SOFIA BETTENCOURT & ROBERT GILLETT:

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