Assessing Criticisms of Faunal Analyses and Environmental Reconstructions in the Tehuacan Valley Project.
Fennell, Christopher C.
Christopher C. Fennell [1]
INTRODUCTION
This comment examines a portion of the statistical data compiled
and analyzed by Flannery (1967) in his archaeological work at Coxcatlan
Cave and other caves near Tehuacan in the early 1960s. The Tehuacan
Valley project was undertaken by MacNeish, Flannery, and others to
establish a chronological, cultural phase, and climatic sequence for
prehistoric periods in this region of Mexico. This large-scale research
project covered a time period spanning approximately 30,000 years to the
present, including phases referred to as the Ajuereado (starting at
30,000 B.C. [+ or -] 10,000), El Riego (8650 B.C. [+ or -] 2000),
Coxcatlan (5705 B.C. 500), and Abejas (3825 B.C. [+ or -] 300, and
ending 2600 B.C. [+ or -] 200) (MacNeish, 1997, pp. 666-670).
The Tehuacan Valley project received pointed criticism from Hardy
(1999, 1996), who focused her doctoral dissertation on reevaluating the
extensive data and the related chronological analyses formulated by
MacNeish, Flannery, and others. Hardy (1996, p. 700) emphasized the
prominence of the Tehuacan Valley project's chronological sequences
within the field of Mesoamerican archaeology, and this provided a
primary impetus for her critical review of the data and related
interpretations. This comment evaluates Hardy's criticisms, and
concludes that she applied an inappropriate statistical test in her
evaluation of Flannery's analysis of rodent remains and related
inferences of environmental changes over time. In contrast, Flannery
(1967) applied statistical tests appropriate to the types of data used
in his analysis, if those data in fact comprised a random sample. The
most intriguing issues in this debate concern Flannery's
propositions that certain natural processes can serve as a proxy for
creating statistica lly random samples, and those samples can then be
used in formulating chronologies of past environmental changes.
BACKGROUND
Among a variety of research efforts in this multiyear project,
Flannery (1967) analyzed the remains of rodents excavated from a series
of strata in various caves near Coxcatlan and Tehuacan, and related the
varying frequencies of the presence of different rodent species to
changes in climatic conditions over time. These rodent remains were
deposited in the caves by owls, whose diet was deemed to
"constitut[e] a random sample of the local rodent population"
(Flannery, 1967, P. 140). After swallowing the rodent whole, the owls
regurgitated "pellets" of the bones and skin particularly
amenable to statistical analysis:
Owls occupied the Tehuacan caves during periods between human
occupations and left behind a stratified series of disintegrating
pellets which were eventually incorporated into the human refuse. These
constitute a series of random samples of the available rodent population
during all periods of prehistory, an almost too-perfect situation for
statistical analysis. (Flannery, 1967, pp. 140-141)
He based this position on his observation that "[t]here is no
evidence that owls discriminate against certain species of rodents, and
hence their diet constitutes a random sample of the local rodent
population" (1967, p. 140). His team excavated approximately 538
rodent bones, which they interpreted as comprising approximately 188
identifiable individuals, from 48 stratigraphic and site locations,
which they categorized by 21 prehistoric time zones (referred to as
preceramic zones) reflected in the stratigraphy. These 21 zones were
grouped into nine broader temporal phases, such as the Early Ajuereado
phase.
Applying a Difference of Proportions statistical test to data that
indicated differences in the presence of various rodent species over
time, Flannery (1967, p. 144) concluded that the "rodent
population, and presumably the environment as well, were significantly
different" during certain phases, and contended the statistical
data on differential frequencies of rat species over time were evidence
of a corresponding difference in climatic conditions in the region over
time. Using these and other faunal data, Flannery inferred that the
climate in the Tehuacan Valley was more arid in an early temporal phase,
referred to as the Early Ajuereado, than previously posited. Such a
difference in climatic conditions provided indicators of the past
habitat in which human populations subsisted. For example, Flannery
(1967, p. 144) believed the absence of cotton rats in the Early
Ajuereado indicated that at that time "[t]he valley floor would
have been open steppe, grazed by horse and antelope, but to judge by the
lack of cotton rats, it could not have had a very rich cover of tall
weeds or grass."
In her reevaluation of the prehistoric sequence formulated in the
Tehuacan Valley project, Hardy criticized the analysis of stone tools
conducted by MacNeish and others, the faunal and related environmental
analysis by Flannery, and the precision and consistency of the
stratigraphic and chronological sequences they formulated. She tested
the statistical significance of Flannery's rodent population data
by running a "Kolmogorov-Smirnoff (sic) test on all five
microfaunal species present in the preceramic zones at Coxcatlan
Cave" (Hardy, 1996, p. 705). Hardy's results indicated that
there was not sufficient statistical significance in rodent population
differences to warrant Flannery's conclusions. He responded that
his data and conclusions remain sound, and that Hardy's
reevaluation should be rejected (Flannery, 1997).
Hardy criticized Flannery's analysis on three main grounds:
the data on rodent species involved too small a sample to be useful;
there were no statistically significant differences in these rodent
populations even using Flannery's data; and the rodent species on
which he based his analysis were not "diagnostic" of past
environmental conditions (Hardy, 1996, pp. 703-705). This comment
addresses the following issues: First, was Flannery correct in his
assumption that the manner of deposition of rodent remains by owls
constituted a random sample that was well-suited to statistical
analysis? Second, was Flannery's use of a Difference in Proportions
test appropriate for these data? Third, was Hardy's use of the
Kolmogorov--Smirnov test appropriate for these data? Finally, can one
use a statistically significant difference in rodent populations as a
basis for making inferences on past climatic conditions in the manner
undertaken by Flannery?
SUMMARY OF RELEVANT DATA
The data on rodent remains from the Coxcatlan and Tehuacan area
caves were set out in detail in Flannery's publication of his
findings (1967, pp. 142-143, Table 15). The data consisted of 48 cases,
each case representing the location of owl pellets containing rodent
remains in a specific stratigraphic zone within a specific site. Seven
types of rodent species were located in these sites: deer mouse, wood
rat, spiny mouse, kangaroo rat, cotton rat, harvest mouse, and pygmy
mouse. In summary, a total of 188 individuals uncovered in these 48
locations consisted of 28 deer mice, 40 wood rats, 36 spiny mice, 27
kangaroo rats, 55 cotton rats, 1 harvest mouse, and 1 pygmy mouse.
Flannery (1967, pp. 142-143, Table 15) divided these 48 specific
stratigraphic zones containing rodent remains into nine temporal phases.
ASSESSMENT
Sample Size and Randomness
Flannery (1967, PP. 140-141) contended in his analysis that the
remains of these individual rodents deposited by owls in caves provided
a sample of adequate size and statistical randomness. He thus utilized
the entire data set of rodent remains uncovered in these caves as a
sample from which to extrapolate an estimate of the relative proportions
of the entire populations of each rodent species in past periods in that
region. He was not seeking to estimate with precision the exact
population counts for each rodent species, but rather to draw inferences
as to their relative presence or absence in the environment. From this,
he sought to infer characteristics, such as aridity, of the environment
at different periods.
One of the more deficient methods for creating a sample is for the
analyst purposefully and subjectively to select those variates she or he
wishes to include in the sample, based on some working sense of
observable patterns. This approach introduces the bias of the analyst
directly into the composition of the sample, and is not replicable due
to its idiosyncratic character. Flannery avoided such a subjective
approach for creating a sample by utilizing the entire set of rodent
remains uncovered, which were deposited by owls (particularly Tyto alba,
the common Barn Owl), as the equivalent of a random sample. He proceeded
on the assumption that the behavior of past owl populations in
targeting, capturing, and consuming different species of rodents was a
direct proxy for a recognized device of selecting a random sample from a
population. He stated that "[t]here is no evidence that owls
discriminate against certain species of rodents" (1967, p. 140). In
his response to Hardy's criticisms, he emphasized this point again:
"Regardless of the routes flown by individual owls, such pellet
samples are archaeologically valuable because owls eat all small rodents
in the region, not just the ones humans like" (Flannery 1997, p.
661, emphasis in original). However, Flannery did not cite any sources
or data to substantiate these statements on the behavior of owls and
rodents that existed several thousand years ago.
Difficulties in the character of Flannery's sample directly
impact the types of tests that can be applied and the inferences one can
derive. The statistical definition of a random sample is not simply a
collection of cases selected through some agency other than the
analyst's personal biases: "[s]pecifically, each element in
the population must have had an equal and independent chance for
selection" (Thomas, 1986, p. 340, emphasis in original). In the
absence of a valid random sample, numerous types of statistical tests
cannot be applied to the data in a valid or meaningful way. Such
statistical methods include the Difference of Proportions test applied
by Flannery and the Kolmogorov--Smirnov test applied by Hardy.
One difficulty in assessing the randomness of the owl deposits as a
sample of the overall rodent populations is that we do not have
sufficient information on either the feeding habits of the owls or the
presence of different types of rodent species within the owls'
range. The sample used consists of only those rodents captured by owls
and then deposited in the caves. This raises a number of questions
concerning the sample. Were there any patterns in the locations in which
owls captured and consumed rodents and later regurgitated rodent
pellets? Did any differential foraging habits of the different species
of rodents tend to make them more vulnerable to being captured and
consumed by owls? Were there any cyclical aspects to the behavior of the
owls or particular rodent species that would create nonrandom patterns
in the sample? Any of these factors could significantly lessen
one's ability to assume there is an independence of events in each
selection of a representative of a particular rodent species by a hunt
ing owl from the general populations that existed in that area (see,
e.g., Bernard, 1995, pp. 81-83; Thomas, 1986, p. 340).
A number of studies of owl predation patterns support the
proposition that the Barn Owl (Tyto alba) is typically nondiscriminatory
in its hunting practices, and that the contents of its pellets should
therefore accurately reflect the relative proportions of the populations
of varying small mammal species that were present in its local habitat
(e.g., Bunn et al., 1982, p. 82; Mikkola, 1983, p. 47; Ticehurst, 1935).
Other studies found that the Barn Owl's pellets do not accurately
reflect the proportions of those populations of prey species (e.g.,
Bellocq, 1998; Wallick and Barrett, 1976; Yom-Tov and Wool, 1997). In
particular, the Barn Owl's predation patterns will be skewed when
species of voles (Microtus) and shrews (Sorex) are present, with those
prey being overrepresented in owl pellets and other species of mice and
rats being underrepresented relative to actual populations (Andrews,
1990, pp. 178-180; de la Torre, 1990, p. 160; Derting and Cranford,
1989; Fast and Ambrose, 1976; Glue, 1974; Herrera and Ja ksic, 1980;
Johnsgard, 1988, pp. 100-101; Taylor, 1994, pp. 77-79; Voous, 1988, pp.
16, 18).
The reports of Flannery (1967) and others in the Tehuacan Valley
project do not indicate the frequencies, if any, with which vole and
shrew remains were uncovered in different time periods and localities
included in their investigations. General studies of the zoological and
geographic characteristics of vole species over time indicate that their
populations have been present in varying ecological habitats in North
and Central America from the Pleistocene period to the present day
(Elton, 1942, p. 104; Hoffman and Koeppl, 1985, pp. 105-113). However,
more specific studies of modern populations indicate that the presence
and range of Microtus species have been much more limited in the areas
of Central and South America than in North America and Europe (Bellocq,
1998; Bunn et al., 1982, p. 82; Herrera and Jaksic, 1980). A modern
sample of over 460 individual rodents contained in owl pellets collected
in the Cueva de los Afligidos cave in the Oaxaca Valley region of Mexico
yielded no Microtus or Sorex specimens (Flannery and Wheeler, 1986). It
is possible that populations of voles and shrews may have been very low
or nonexistent in the specific habitat zones and time periods
investigated by Flannery and his colleagues within the Tehuacan Valley
region. In the absence of significant populations of voles or shrews,
Barn Owls have a greater tendency to prey on the diversity of other
rodent species in a nondiscriminatory manner, and to produce pellets
that would reflect the relative proportions of those other species'
populations in the local habitat (see, e.g., Taylor, 1994, pp. 36-37,
80-81).
Flannery has been sensitive to issues concerning possible skewing
in deposition behavior in other studies. For example, he observed
elsewhere a differential presence of domesticated or wild food products
that people brought to caves and consumed at those locations. In such
instances, the samples of proportions from each type will be distorted
and inferences must be undertaken with great caution, if at all
(Flannery, 1976, p. 116). Thus, without additional supporting data, the
unknown capture, consumption, and regurgitation behavior of past owl
populations cannot serve as a proxy for rigorous methods of selecting
random samples.
Flannery proposed to use all of the rodent remains uncovered in the
Tehuacan Valley project as a sample of the extrapolated, inferred
populations of rodents existing in the region in these past time periods
rather than take an even smaller sample from this sample. However, an
inference of which populations of species were larger or smaller
relative to one another depends upon the ability to infer the size of
each population to estimate those proportions. Therefore, one cannot
dependably make an inference of overall population sizes based on his
chosen sample.
If Flannery's sample was not random and probabilistic, what
was it? The closest category is that of "convenience or haphazard
sampling," in which the analyst uses as a sample those cases that
present themselves for recording in some convenient manner. However,
such a convenience sampling method should be used as a preliminary step
only, and not as a sample from which one would attempt to draw
inferences. Basing strong inferences on such a convenience sample is
"plain hazardous" in terms of statistical rigor (Bernard,
1995, p. 94). In the absence of a probabilistic sampling, principles of
statistics dictate that one should not generalize beyond the sample
(Bernard, 1995, p. 96).
Hardy (1996) focused her criticisms on the small size of the
sample, a characteristic that also affects the likelihood that the
sample was random.
The equal probability of any one individual rodent being selected
by an owl from the general population would be lessened and distorted if
the overall population was small, and thus the resulting sample was
small. Neither Flannery nor Hardy discuss any measures that may have
been taken to correct for such possible distortions in the randomness of
the sample due to a small population and associated sample. This would
likely be difficult in any event, since Flannery did not have data
indicating the sizes of the overall populations. He could only
extrapolate those population sizes based on the limited sample exhibited
in the archaeological record uncovered in the caves.
Applying the Difference in Proportions Test
Flannery's application of a Difference of Proportions test to
the data on the frequency with which different species of rodents
appeared in the various strata and time periods was inappropriate.
Although this test may be conducted on nominal data, one must utilize a
random sample to conduct a Difference of Proportions test. For the
reasons discussed earlier, the sample utilized by Flannery should not be
assumed to be the equivalent of a random sample. However, for the sake
of argument and further analysis, this comment will assume that this
sample was random. The Difference of Proportions test can then be
conducted, using the different percentages of each species'
presence in each temporal phase. This was the test Flannery conducted,
using an alpha ("[alpha]") value of .01 (1967, p. 144).
Specifically, Flannery compared the percentages of the presence of
cotton rat, kangaroo rat, and deer mouse in the Early Ajuereado time
period (30,000 B.C. [+ or -] 10,000) to the presence of each of those
species in the post-Pleistocene period. He used the term
"post-Pleistocene" to be equivalent to "Present Climatic
Conditions" (1967, pp. 142-144). Flannery (1967) did not set forth
the exact calculations he applied. Assuming he applied the standard
formula for the Difference of Proportions test, his calculations should
have been based on a null hypothesis ("[H.sub.0]") that the
proportions of a given rodent species present in the Early Ajuereado
phase are equal to the proportion of that same species present in the
post-Pleistocene (or "[micro]1 = [micro]2"). The alternative
hypothesis [H.sub.a] is that these proportions are not equal (or
"[micro]1 [not equal to] [micro]2"). The formula is as
follows:
Z = ps1 - ps2/ops1 -ps2
Where
Ops1 - ps2 = [square root]pu qu X [N.sub.1] +
[N.sub.2]/[N.sub.1][N.sub.2]
Where
[P.sub.u] = [N.sub.1][p.sub.1] + [N.sub.2][p.sub.2]/[N.sub.1] +
[N.sub.2] and [q.sub.u] = 1 - [p.sub.u].
We will reject the null hypothesis [H.sub.0] if Z [greater than]
Z[alpha], or if [alpha] [greater than] the actual "p" value,
where [alpha] equals .01, and the actual p value equals .5 - Z[alpha].
Applying the Difference of Proportions test to each case shows that
we can reject the null hypothesis as to the cotton rat (Z = 2.9566) and
the deer mouse (Z = 5.5526). We can therefore conclude that the
proportions of each of these species present in the Early Ajuereado
phase were not equal to those proportions present in the
post-Pleistocene period. These test results support Flannery's
conclusion that the cotton rat was notably absent, and the deer mouse
notably present, in the Early Ajuereado phase as compared to the
post-Pleistocene (1967, p. 141). However, the null hypothesis cannot be
rejected for the kangaroo rat (Z = 1.8826), wood rat (Z = 1.7485), spiny
mouse (Z = 1.6225), harvest mouse (Z = .3364), or pygmy mouse (Z =
.3364).
Flannery (1967) applied the Difference of Proportions test to the
data for the cotton rat, kangaroo rat, and deer mouse, but did not apply
it to the data for the wood rat, spiny mouse, harvest mouse, and pygmy
mouse. Having applied the same test to these latter species, it is
notable that the null hypothesis of equal proportions over time cannot
be rejected for five of the seven species of rodents on which his
analysis focused. This does not necessarily weaken the findings for the
cotton rat and deer mouse under the Difference of Proportions test.
However, it is an additional indicator that there may be flaws in the
assumption that owl deposition of rodent remains was the equivalent of a
random sample. The differential shifts, or lack of shifts, in the
proportions of each species' presence may reflect some form of
discriminatory consumption by owls over time, rather than changes in the
population sizes of each species.
Hardy's Use of the Kolmogorov-Smirnov Test
Hardy's application of the Kolmogorov-Smirnov test to
Flannery's data was inappropriate. The Kolmogorov test was designed
for application to ordinal data and random samples (see, e.g., Shennan,
1997, pp. 55, 57, 65; Siegel, 1956, pp. 48-51, 135-136; Thomas, 1986, p.
336). Flannery's data were nominal in nature, consisting of counts
of individuals, fitting each exclusively into one of seven
classifications of rodent species at each site and stratum. There was no
ordering of the data to provide an ordinal scale, nor was there any
equal unit of measure between variates to provide an interval scale
(see, e.g., Thomas, 1986, pp. 19-26). Flannery's rodent data did
not contain ordinal characteristics to which the Kolmogorov-Smirnov test
could be applied with any valid statistical meaning.
It is curious that Hardy applied the Kolmogorov test to
Flannery's data after contending that the sample was too small to
be useful or random. She also provided no indication that she considered
attempting to convert (or in fact converted) the original nominal data
into an ordinal data form for the purpose of conducting this type of
test. Hardy instead applied the test to the wrong type of data, and to
what she believed to be the wrong type of sample. Could the rodent count
data be converted into a useful form of ordinal data? No: the data
presented do not include any characteristic that can be used for
establishing a meaningful property of asymmetry (see Siegel, 1956, pp.
23-26; Thomas, 1986, P. 22). Flannery's data on the presence or
absence of each of these different rodent species do not yield to a
meaningful ordinal seriation of the separate species. While one might
speculate as to a particular, asymmetrical relation between two of these
species (e.g., C[greater than] F), one cannot line them all up in a
meaningful continuation of ranked gradation so that A [greater than] B
[greater than] C [greater than] D [greater than] E [greater than] F
[greater than] G.
Extrapolations for Climatic Conditions
It is hazardous to make robust extrapolations from nonrobust,
non-parametric statistical tests. An additional step for Flannery's
analysis was the ability to treat the relative differences of rodent
populations as diagnostic of different environmental conditions. This is
an issue of anthropological and environmental science, and not of
statistical theory. Flannery provided little or no discussion of sources
for his confidence that such rodent population differences were
diagnostic. Hardy criticized his assumption by offering comparably
sweeping statements of rodent population tendencies without supporting
sources. Absent solid support for this assumption of diagnostic
significance, Flannery's anthropological conclusions are
substantially weakened.
However, Flannery's use of inferences from the rodent remains
was not critical to his overall analysis. His inferences on past
climatic conditions were based on a variety of faunal remains uncovered
in these extensive excavations, including deer, jack rabbit, Mexican
cottontail, and iguana (1967, p. 144). The data on rodent remains thus
provided additional support to his overall analysis, and were not used
in isolation.
CONCLUSIONS
Hardy's criticisms of the value and validity of
Flannery's rodent populations analyses fail. She brought no new
excavation findings to bear on this debate. Rather, she focused solely
on undertaking a critical review of the data compiled and analyzed by
those whose conclusions she sought to disprove. Yet she applied
incorrect tests and failed adequately to consider and question all of
the assumptions concerning the nature of the data under examination.
Flannery's proposed proxy for a random sample remains
intriguing: Can a naturally-occurring process, such as owl deposition of
rodent remains, be used as the equivalent of a random sample? Thus far,
it appears to be a questionable proposition. However, to date there is
no definitive empirical evidence offered by proponents or detractors by
which to conclude if the typical behavior of rats, mice, and owls could
have resulted in such convenient randomness.
ACKNOWLEDGMENTS
The author thanks Kent Flannery, Karen Hardy, and Rachel Most for
their helpful comments and critiques of earlier versions of this
commentary. Any shortcomings remain the author's responsibility.
(1.) Department of Anthropology, University of Virginia,
Charlottesville, Virginia.
REFERENCES
Andrews, P. (1990). Owls, Caves and Fossils: Predation,
Preservation and Accumulation of Small Mammal Bones in Caves, With an
Analysis of the Pleistocene Cave Faunas From Westburysub-Mendip,
Somerset, UK, University of Chicago Press, Chicago.
Bellocq, M. I. (1998). Prey selection by breeding and nonbreeding
Barn Owls in Argentina. The Auk 115(1): 224-229.
Bernard, R. (1995). Research Methods in Anthropology, AltaMira
Press, London.
Bunn, D. S., Warburton, A. B., and Wilson, R. D. (1982). The Barn
Owl, Buteo Books, Vermillion, SD.
de la Torre, J, (1990). Owls: Their Life and Behavior, Crown, New
York.
Derting, T. L., and Cranford, J. A. (1989). Physical and behavioral
correlates of prey vulnerability to Barn Owl (Tyto atba) predation.
American Midland Naturalist 121(1): 11-20.
Elton, C. (1942). Voles, Mice and Lemmings: Problems in Population
Dynamics, Oxford University Press, Oxford.
Fast, S. J., and Ambrose, H. W., III (1976). Prey preference and
hunting habitat selection in the Barn Owl. American Midland Naturalist
96(2): 503-507.
Flannery, K. V. (1967). The vertebrate fauna and hunting patterns.
In Byers, D. S. (ed.), The Prehistory of the Tehauacan Valley, Vol. 1,
Environment and Subsistence, University of Texas Press, Austin, TX, pp.
132-177.
Flannery, K. V. (1976). Empirical determination of site catchments
in Oaxaca and Tehuacbn. In Flannery, K. V. (ed.), The Early Mesoamerican
Village, Academic Press, New York, pp. 103-116.
Flannery, K. V. (1997). In defense of the Tehuacan Project. Current
Anthropology 38(4): 660-662.
Flannery, K. V., and Wheeler, J. C. (1986). Comparing the
preceramic and modern microfauna. In Flannery, K. V. (ed.), Guild
Naquitz: Archaic Foraging and Early Agriculture in Oaxaca, Mexico,
Academic Press, New York, pp. 239-246.
Glue, D. E. (1974). Food of the Barn Owl in Britain and Ireland.
Bird Study 21(3): 200-210.
Hardy, K. (1996). The preceramic sequence from the Tehuacan Valley:
A reevaluation. Current Anthropology 37(4): 700-716.
Hardy, K. (1999). On the Tehuacan Project: Reply to Flannery and
MacNeish. Current Anthropology 40(1): 63-69.
Herrera, C. M., and Jaksic, F. M. (1980). Feeding ecology of the
Barn Owl in Central Chile and Southern Spain: A comparative study. The
Auk 97(4): 760-767.
Hoffman R. S., and Koeppl, J. W. (1985). Zoogeography. In Tamarin,
R. H. (ed.), Biology of New World Microtus. The American Society of
Mammalogists, Shippensburg, PA, pp. 84-115, Special Publication No. 8.
Johnsgard, P. A. (1988). North American Owls: Biology and Natural
History, Smithsonian Institution Press, Washington, DC.
MacNeish, R. S. (1997). In defense of the Tehuacan Project Current
Anthropology 38(4): 663-672.
Mikkola, H. (1983). Owls of Europe, Buteo Books, Vermillion, SD.
Shennan, S. (1997). Quantifying Archaeology, University of Iowa
Press, Iowa City.
Siegel, S. (1956). Nonparametric Statistics for the Behavioral
Sciences, McGraw-Hill, New York.
Taylor, I. (1994). Barn Owls: Predator-Prey Relationships and
Conservation, Cambridge University Press, Cambridge.
Thomas, D. H. (1986). Refiguring Anthropology, Waveland Press,
Prospect Heights, IL.
Ticehurst C. B. (1935). On the food of the Barn Owl and its bearing
on Barn Owl population. The Ibis 5(2 Serial no. 13): 329-335.
Voous, K. H. (1988). Owls of the Northern Hemisphere, MIT Press,
Cambridge.
Wallick, L. G., and Barrett, G. W. (1976). Bioenergetics and prey
selection of captive Barn Owls. The Condor 78(1): 139-141.
Yom-Tov, Y., and Wool, D. (1997). Do the contents of Barn Owl
pellets accurately represent the proportion of prey species in the
field? The Condor 99(4): 972-976.