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Ye Pleasant Mount: 1989 1990 Excavations - Open site which ...

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specimens that have been studied by these institutions to produce the allometric values in<br />

Table 1.<br />

There are inherent problems with biomass as well. The most apparent is that<br />

archeological bone weight is affected by a wide range of factors that can skew the biomass<br />

calculation (i.e., alterations occurring to the bone during processing for food or other uses<br />

and during archeological deposition). Further, just as MNI emphasizes small species,<br />

biomass emphasizes larger species by focusing attention on weight.<br />

Sample size biases can affect both MNI and biomass calculations. Some researchers<br />

have suggested that a sample of at least 200 individuals (MNI) or at least 1400 identifiable<br />

bone fragments is necessary for reliable interpretations of a faunal assemblage (Grayson<br />

1981; Wing and Brown 1979). Smaller samples may suggest inaccurate interpretations of<br />

the composition of taxa at a <strong>site</strong>. A certain taxon that may appear abundant in a small<br />

sample may in actuality be less significant when a larger sample from the same <strong>site</strong> is<br />

examined. Grayson (1984:129) showed that the apparent taxonomic abundance ofa species<br />

in a faunal assemblage may be more a function of sample size than actual population size<br />

and <strong>site</strong> utilization.<br />

In recent years paleontologists, zooarcheologists, and archeologists have been paying<br />

more attention to <strong>site</strong> formation process that affect bone as it enters the archeological or<br />

paleontological record. Taphonomy, "the science of the laws of embedding" as first<br />

discussed by Efremov (1940), has become an important methodology for consideration in<br />

studying vertebrate fauna. Several researchers have written about the influence of<br />

taphonomic process on archeological bone (Behrensmeyer and Hill 1980; Binford 1981;<br />

Brain 1981; and Gifford 1978).<br />

Many human and non-human influences affect pre-and post-depositional bone.<br />

Before deposition, butchering practices and other food processing and cooking methods,<br />

can alter the original shape and chemical composition of the bone. Bone that has been<br />

cooked, smoked, or chemically treated may be weakened by these processes and made<br />

more susceptible to decomposition. Disposal habits can further alter the bone assemblage<br />

recovered from a <strong>site</strong>. Not all bones that are butchered enter the ground simultaneously<br />

and once the bones are discarded they may be trampled by humans and other animals.<br />

Plowing, exposure to the sun, and other weathering forces such as the pH level of the soil<br />

continue the differential dispersal and decomposition of the bone. Gnawing by rodents and<br />

carnivores is another factor to consider in examining bone depositional processes. For <strong>site</strong>s<br />

containing large amounts of shell, the calcium in the shell serves as a medium that helps<br />

to preserve bone. The density of the bone itself is also an important criterion in bone<br />

preservation (Grayson 1984:25). Teeth, metapodials, and phalanges often preserve better<br />

because they are small, dense bones (Lyman 1985). It is also important to recognize that<br />

many bones that enter the archeological record do not represent food activities. Some<br />

bone results from fur exploitation, hide tanning or bone working. Exposed garbage,<br />

3

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