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Ethnoecology, Resource Use, Conservation And Development In A ...

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that strongly indicate prior unsustainable levels of exploitation (chapters 4.5.1,<br />

8.1.5). <strong>In</strong> each of these examples, however, the reported decline has been of a very<br />

large magnitude. My overall impression is that it is only in such dramatic cases can<br />

ethnoecology, used in isolation, provide a reliable indication of sustainability. <strong>In</strong> most<br />

circumstances it must also be employed in conjunction with scientific methods.<br />

Evaluation of sustainability in scientific ecology generally takes the form of<br />

observations of changes in abundance of animals. This may be either sightings per<br />

unit survey effort or, in the case of exploited populations, catch per capture unit<br />

effort. This is essentially a formalisation of the method employed by people in<br />

observing the declines in abundance of particular species reported above. <strong>In</strong> the<br />

informal case, the accuracy is limited by the unreliability of human memory -<br />

perceptions of abundance will generally be very impressionistic, and memories of the<br />

time-scales over which they occur unreliable. Scientific biology collects such<br />

observations in a systematic and accurate fashion, such that their precision and utility<br />

are far greater, and thus provides a more powerful framework for their recording and<br />

analysis. This approach can, in turn, be enhanced by the particular contributions that<br />

ethnoecology has to make.<br />

Most importantly, hunting activity itself can provide an opportunity for data<br />

collection. Collection and measuring of skulls provided by hunters, in connection with<br />

interview data, was successfully incorporated into a study of Ebolo hunting behaviour<br />

(Dwyer 1990). Both the accuracy and the extent of hunters' participation in such a<br />

programme can be enhanced if hunters maintain their own records of hunting trips,<br />

sightings and successful kills (Bodmer and Puertas 2000). The body of data collected<br />

can be enhanced by the incorporation of observations of tracks and other animal<br />

signs, of which local hunters are invariably the most proficient observers and<br />

interpreters (Hill et al. 1997). Further, as shown in this study, ethnoecology can<br />

provide highly detailed local information on habitat use, seasonal movements and<br />

responses to predators and competitors of hunted animals, all of which factors would<br />

need to be incorporated into the data collection and analysis regimes of a monitoring<br />

programme.<br />

This thesis has thus confirmed and advanced the arguments of several previous,<br />

less extensive studies. First, that ethnoecological knowledge incorporates a large<br />

quantity of information that can be used to generate biological data (Townsend<br />

1995; Ponte Johansons 1995; Ferguson et al. 1998; Myrmin et al. 1999; Huntington<br />

et al. 1999). That ethnoecology and scientific ecology therefore possess a<br />

substantial area of common ground (cf. Agrawal 1995), but also, and crucially, differ

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