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Pre-Colombian Jamaica: Caribbean Archeology and Ethnohistory

by Phillip Allsworth-Jones

by Phillip Allsworth-Jones

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170 / Appendix A.<br />

with an MNI of 747. The figures for MNI have been taken or calculated from<br />

her report, <strong>and</strong> the percentages of the classes represented have been recalculated<br />

(in view of some apparent discrepancies in individual percentages as printed in<br />

her report). Clearly, fish are dominant, closely followed by crabs. As Scudder<br />

comments, the most abundant fish taxa are “representatives of families which<br />

utilize both reef <strong>and</strong> open- bottom areas in shallow near- shore environments.”<br />

Individual bird frequencies are not specified, but they included egrets, herons,<br />

doves, pigeons, seagulls, <strong>and</strong> clapper rails. As Scudder remarks, when the frequencies<br />

are broken down level by level, some interesting shifts in faunal exploitation<br />

through time emerge (Scudder 1992:Figure 2). In general, there is a<br />

tendency for fish to increase <strong>and</strong> for crabs to decrease, <strong>and</strong> the mollusks closely<br />

track the fish values.<br />

Scudder concludes that “the overall faunal assemblage depicts a localised exploitation<br />

of typical West Indian dry- coastal <strong>and</strong> shallow- water animal communities.”<br />

It indicates a “restricted catchment area,” with an absence of distant<br />

montane <strong>and</strong> pelagic species. In comparison with both White Marl (S1)<br />

<strong>and</strong> Bellevue (K13) one can detect “a clear continuum of coastal to inl<strong>and</strong> localised<br />

adaptation.” The three sites are shown on Scudder’s map, which also<br />

has the merit of indicating the different types of shoreline on the isl<strong>and</strong> (Appendix<br />

43).<br />

While this general conclusion is convincing, there are some difficulties in<br />

using Scudder’s figures as published for comparative purposes. There are two<br />

reasons for this. First, MNI <strong>and</strong> percent figures are not given for all the species<br />

represented at Rodney’s House, as is clear from Table 25. Second, her figures<br />

include crabs <strong>and</strong> lobsters, of which there are 17 specimens, or 23 percent,<br />

of the total MNI at the site (Scudder 1992:38). At White Marl (S1) <strong>and</strong><br />

at Bellevue (K13), unfortunately, no information of this kind is available, even<br />

though crabs were certainly present (Silverberg et al. 1972:Table 2, note*). The<br />

breakdown of species represented at Rodney’s House according to “resource<br />

use areas” <strong>and</strong> in terms of percent of total MNI is as follows (Scudder 1992:<br />

Figure 3). Figures for actual MNI have been calculated on the assumption that<br />

total MNI = 747, see Table 19.<br />

Clearly, the terrestrial element includes the majority of the mammals (excepting<br />

manatee) <strong>and</strong> the birds (as at White Marl) as well as iguana. Scudder<br />

indicates that the two l<strong>and</strong> crabs Cardisoma <strong>and</strong> Gecarcinus are also included,<br />

although (if so) this would seem to produce too big a total. The beach element<br />

clearly includes sea turtles, although elsewhere it is said that no pelagic species<br />

are present. Inshore elements include manatees <strong>and</strong> crocodiles, <strong>and</strong> also certain

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