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Prehistoric economies during the Late of the Potomac Valley: An examination of animal resource utilization

Moore, Elizabeth Ann, Ph.D.

The American University, 1994

Copyright ©1994 by Moore, Elizabeth Aim. All rights reserved.

UMI 300 N. ZeebRd. Ann Aibor, MI 48106

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. PREHISTORIC ECONOMIES DURING THE LATE WOODLAND PERIOD

OF THE POTOMAC VALLEY: AN EXAMINATION OF

ANIMAL RESOURCE UTILIZATION

by

Elizabeth A. Moore

submitted to the

Faculty of the College of Arts and Sciences

of The American University

in Partial Fulfillment of

the Requirements for the Degree

of

Doctor of Philosophy

in

Anthropology

Signatures of Committee:

Chair:

<4

. l^ r

Jean of'the College

Date

1994

The American University

Washington, D.C. 20016

THE AMERICAN UNIVERSITY LIBRARY

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. © COPYRIGHT

by

ELIZABETH A. MOORE

1994

ALL RIGHTS RESERVED

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. To my Mother

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. PREHISTORIC ECONOMIES DURING THE LATE WOODLAND PERIOD

OF THE POTOMAC VALLEY: AN EXAMINATION OF

ANIMAL RESOURCE UTILIZATION

BY

Elizabeth A. Moore

ABSTRACT

This research describes differences in the prehistoric economies of two

Late Woodland archaeological cultures, the Montgomery Complex and the

Luray Focus, and examines the relationship between these differences and

other sociocultural factors. Zooarchaeological data used to perform this

examination were collected from six sites. The relative completeness and

research utility of all assemblages was determined. Other artifact classes and

site features were described to provide a more complete view of these sites.

The zooarchaeological data was used to define four key aspects of

hunting strategies - the diversity of vertebrate taxa exploited, the habitats which

were exploited to acquire those taxa, the exploitation of seasonally available

resources, and the techniques used to hunt deer. At the sites from the

Montgomery Complex, a wide variety of taxa were hunted or collected from all

of the surrounding habitats. Deer were hunted with a specific strategy at the

ii

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Rosenstock site, a strategy that resulted in the killing of the age groups that

were of maximum meat-yielding age and size. Seasonally abundant resources

were targeted for exploitation as they became available. As an overall pattern,

the occupants of the Montgomery Complex sites appear to have been

maximizing the exploitation of many of the animal resources found in the area.

The hunting strategies at sites from the Luray Focus contrast to those

from the Montgomery Complex in several ways. First, only a limited number of

animal taxa were being hunted or collected. These taxa were probably found in

the gardens or garden borders. Second, the seasonally available resources in

the area were not targeted for maximum exploitation. The presence of

seasonally available resources in the assemblages is marginal and their

collection was probably opportune and not necessarily part of a deliberate

strategy to exploit those particular taxa.

Several sociocultural factors that may be related to these differences in

hunting strategies are examined. These factors include a possible increase in

the dependence upon cultivars, an increase in the use of defensive

fortifications, and differences in stalking techniques for deer hunting. Finally,

the implications of the relationship between these factors and the differences in

the overall economies as reflected in the hunting strategies are discussed.

in

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. ACKNOWLEDGEMENTS

This research project has benefitted from the input of numerous

individuals. Professors, colleagues, friends, and family all provided the support

without which this work could not have been possible. Any errors in this work

have occurred in spite of their assistance.

First, I would like to thank my committee members. My advisor Richard

J. Dent not only provided the faunal material from the Hughes site but also

critiqued the results of my work. Charles W. McNett, Jr. shared a great deal of

his time and knowledge as well as a good portion of his library. June Evans

has been an inspiration to me both personally and professionally. I especially

appreciate her steady reminders to take time away from work and writing to

enjoy my family. Last, but certainly not least, I owe a special debt to Melinda

A. Zeder. She introduced me to zooarchaeology and provided invaluable

training and support through this entire process. In particular, her critical (and

sometimes humorous) comments on this research contributed greatly to the

final product.

I thank several individuals at the Maryland Historical Trust, Office of

Archeology. Tyler Bastian, Dennis Curry, and Maureen Kavanagh generously

provided me with the opportunity to analyze the faunal material from the

Rosenstock site. Their comments and input during my all-too-short visits to the

iv

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. site and my assorted trips to the Trust gave me much encouragement.

I thank the Archaeological Society of Maryland for all of the work that

they performed in the field at the Rosenstock site and in the lab after the

excavations ended. Without their continued labor and the assemblage that

resulted from that work, this research would not have been possible.

Bruce D. Smith has provided support and encouragement over the last

several years and for that I am very grateful. In addition, his empathy and

humor regarding the entire dissertation process helped me keep this experience

in perspective.

Susie Arter has been both a dear friend and a valued colleague. Her

tenacity in identifying the most frustrating bone fragment was a great help in the

lab. Justin Lev-Tov was another colleague who provided not only technical

assistance but also friendship. Without his help, I might still be struggling with

the fishes.

I acknowledge several members of my family for their roles in this

project. My mother encouraged me to do exactly what I wanted and I thank her

for telling me not to go to law school. Leah Drown has quite persistently

performed the task of "cracking the whip" and I thank her for not letting me

procrastinate any more than I already did. Sarah Myler provided the loving

support only a sister can.

I have a most heartfelt thanks and acknowledgement for Varna G. Boyd.

As a professional and colleague, the advice, the constructive criticism, the

v

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. editing comments, and the wealth of archaeological experience that she has

shared with me has been invaluable. I thank her for being one of those truly

special friends that few are lucky to find.

Finally, I would like to thank my husband Tim Moore and my daughter

Rebecca Joy Moore. Rebecca has provided the motivation for me to finish as

quickly as possible so that I don't have to devote all of my spare time to my

computer. I thank her for two very important things over the past three months

- arriving after my defense and sleeping through the night. Tim has graciously

suffered through the dissertation process and I thank him for his patience and

his valued comments and advice.

vi

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. TABLE OF CONTENTS

ABSTRACT ...... ii

ACKNOWLEDGEMENTS...... iv

LIST OF TABLES ...... xiii

LIST OF FIGURES ...... xv

CHAPTER 1 INTRODUCTION ...... 1

Statement of the Problem ...... 1

Background ...... 3

Test Implications...... 12

Goals and Objectives ...... 14

Methodology ...... 21

Organization...... 24

Conclusion ...... 26

CHAPTER 2 CULTURE HISTORY...... 28

Introduction...... 28

Montgomery Complex ...... 29

Village Organization ...... 31

Ceramic Artifacts...... 32

Lithic Artifacts ...... 34

Worked Bone and Antler Artifacts ...... 36

vii

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Mortuary Patterns ...... 38

Subsistence Patterns ...... 39

Mason Island Complex ...... 42

Village Organization ...... 43

Ceramic Artifacts...... 43

Lithic Artifacts ...... 44

Worked Bone and Antler Artifacts ...... 45

Mortuary Patterns ...... 45

Subsistence Patterns ...... 45

Luray F o c u s...... 46

Village Organization ...... 47

Ceramic Artifacts...... 52

Lithic Artifacts ...... 56

Worked Bone and Antler Artifacts ...... 59

Mortuary Patterns ...... 62

Subsistence Patterns ...... 66

Discussion ...... 71

Conclusion ...... 85

CHAPTER 3 ASSEMBLAGE RECOVERY AND UTILITY ...... 86

Introduction...... 86

18FR18 - The Rosenstock S ite ...... 94

Excavation, Recovery, and Curation ...... 94

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Assemblage Description...... 96

Summary ...... 98

18M01 - The Hughes S ite ...... 100

Excavation, Recovery, and Curation ...... 100

1937-1938 Excavations ...... 101

1990-1991 Excavations ...... 102

Assemblage Description ...... 104

Summary ...... 106

18M03 - The Shepard Site ...... 107

Excavation, Recovery, and Curation ...... 107

1936-1939 Excavations ...... 108

1952-1955 Excavations ...... 110

1955 Excavations ...... 110

Assemblage Description ...... 111

Summary ...... 112

18M04 - The Shepard Barrack Site ...... 114

Excavation, Recovery, and Curation ...... 114

Assemblage Description ...... 115

Summary ...... 116

18M09 - The Winslow S ite ...... 117

Excavation, Recovery, and Curation ...... 117

1940-1941 Excavations ...... 118

ix

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 1959-1962 Excavations ...... 119

Assemblage Description ...... 122

Summary ...... 122

44PA1 - The Keyser Farm S ite ...... 124

Excavation, Recovery, and Curation ...... 124

Assemblage Description ...... 126

Summary ...... 127

Conclusion ...... 128

CHAPTER 4 ANALYTICAL METHODS ...... 130

Introduction...... 130

Analytical Techniques ...... 131

Aging and Sexing of Specimens ...... 149

D e e r ...... 149

R accoon...... 156

Butchering S c a rs...... 158

Sampling Strategies ...... 159

Primary Material ...... 161

Secondary Material ...... 163

Definitions of Analytical T e rm s ...... 164

NISP ...... 165

MNI ...... 166

MNE ...... 189

x

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Diversity ...... 194

Shannon-Weaver Index ...... 196

Evenness ...... 196

Richness...... 198

Chi-Square ...... 199

Kolmogorov-Smirnov ...... 201

Summary ...... 203

CHAPTER 5 SUMMARY OF DATA ...... 204

Introduction ...... 204

Animal Utilization at Montgomery Complex S ite s ...... 206

Diversity ...... 206

Seasonality...... 216

Animal Selection ...... 220

Animal Processing...... 226

Butchering Patterns ...... 235

Animal Utilization at Luray Focus S ite s...... 238

Diversity ...... 238

Seasonality...... 244

Animal Selection ...... 246

Animal Processing...... 248

Butchering Patterns ...... 252

Comparison of Animal Utilization Patterns at Montgomery Complex and Luray Focus Site s ...... 254

xi

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Diversity ...... 255

Seasonality...... 261

Animal Selection, Processing, andButchering ...... 263

Conclusion ...... 265

CHAPTER 6 CONCLUSIONS...... 268

The Use of Curated Collections ...... 285

Directions for Future Research ...... 286

APPENDIX ONE TABLE 23: TAXONOMIC CLASSIFICATION OF SPECIES RECOVERED ...... 290

APPENDIX TWO TABLE 24: HABITATS FOR SPECIES RECOVERED . . 297

APPENDIX THREE TABLE 25: ODOCOILEUS VIRGINIANUS MANDIBULAR TEETH MEASUREMENTS (BASED ON SEVERINGHAUS 1948) ...... 306

APPENDIX FOUR TABLE 26: BUTCHERING SCAR INVENTORY FOR THE ROSENSTOCK (18FR18) AND HUGHES (18M01) SITES .. 314

BIBLIOGRAPHY...... 332

xii

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. LIST OF TABLES

Table Page

1. Radiocarbon Dates from Montgomery Complex, Mason Island Complex, and Luray Focus S ites ...... 18

2. Burial Data from the Shepard Site (18M03) Compiled from Slattery and Woodward 1992 and MacCord, Schmitt, and Slattery 1957 . . 40

3. Counts and Weights of Specimens by S ite ...... 89

4. Bone Tool (BTI) and Measurable (Ml) Indices ...... 91

5. Number of Taxa Represented at Each S ite ...... 92

6. Faunal Analysis C o d e s...... 136

7. Fragment Orientation for Known Skeletal Element Fragments ...... 150

8. Criteria for Age Classes for Deer ( Odocoileus virginianus) from

Severinghaus 1949 ...... 152

9. Age Classes for Raccoon (Procyon lotor) from Grau, et al. 1970 . . . 157

10. Codes for Butchering Scars...... 160

11. Percentages of Assemblages from the Rosenstock and Hughes Sites Submitted to Each Phase of Analysis ...... 164

12. NISP by Site ...... 167

13. Percent of NISP by Site ...... 172

14. MNI for Identifiable Remains by Site ...... 178

15. Percent MNI for Identifiable Remains by Site ...... 183

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 16. Minimum Number of Elements (MNE) for Deer (Odocoileus virginianus) ...... 191

17. Raccoon MNI by Site and Age C la s s...... 227

18. Distribution of Number of Butchering Scars for Rosenstock (18FR18) and Hughes (1 8 M 0 1 ) ...... 236

19. Distribution of Percentage of Types of Butchering Scars for Rosenstock (18FR18) and Hughes (18M01) ...... 237

20. Shannon-Weaver Index Calculations Comparing Evenness and Richness for the Rosenstock and Hughes S ite s...... 257

21. Kolmogorov-Smirnov Test Calculations for the Distribution of Specimens (NISP) by Class for the Rosenstock and Hughes S ite s ...... 258

22. Chi-Square Calculations for Distribution of Specimens by Class for the Rosenstock and Hughes S ites ...... 260

23. Appendix One: Taxonomic Classification of Species Recovered .... 290

24. Appendix Two: Habitats for Species Recovered ...... 297

25. Appendix Three: Odocoileus Virginianus Mandibular Teeth Measurements (Based on Severinghaus 1948) ...... 306

26. Appendix Four: Butchering Scar Inventory for the Rosenstock (18FR18) and Hughes (18M01) Sites ...... 314

xiv

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Figure Page

1. Study A re a ...... 15

2. Distribution of Dates for Montgomery Complex and Luray Focus S ite s ...... 17

3. Bone Tool and Measurable Bones Indices ...... 99

4. Potomac Valley Faunal Analysis Code Sheet ...... 148

5. Seasonality of Deer Mandibles ...... 218

6. Age Composition of Deer Populations, The Rosenstock Site ...... 222

7. Age Composition of Deer Populations, The Winslow S ite ...... 224

8. Percentages of Deer MNE by Body Part, The Rosenstock Site .... 229

9. Percentages of Deer MNE by Body Part, The Winslow S ite ...... 233

10. Percentages of Deer MNE by Body Part, The Shepard S ite ...... 234

11. Age Composition of Deer Populations, The Hughes S it e ...... 247

12. Percentages of Deer MNE by Body Part, The Hughes Site ...... 249

13. Percentages of Deer MNE by Body Part, The Keyser Farm Site .... 251

14. Percentages of Deer MNE by Body Part, The Shepard Barrack S ite ...... 253

15. Percentages of Deer MNE by Body Part, The Hughes and Rosenstock S ite s...... 264

xv

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. CHAPTER 1

INTRODUCTION

Statement of the Problem

During the Late Woodland period in the Eastern Woodlands, specifically

in the Middle Atlantic region, a number of changes occurred within the

indigenous cultures. Much of the cultural historical and theoretically oriented

literature concerning this period states that beginning at approximately A.D.

1000 an intensification of food production began in the Eastern Woodlands.

This resulted in a shift away from an economic system based primarily on the

hunting and gathering of wild resources toward one that was agriculturally

oriented and based primarily on the cultivation of corn, beans, and squash

supplemented by the collection of wild resources. By A.D. 1200 this

development had resulted in an economy based on a more sedentary way of

life, one increasingly dependent upon cultivated plant resources (Caldwell 1958;

Catlin 1982; Clark 1980; Cohen 1977; Custer 1986; Ford 1985; Griffin 1968;

Kavanagh 1982, 1983; Keegan and Butler 1987; Potter 1982, Smith 1992).

Previous research on this time period in the Piedmont province of the Potomac

Valley has focussed on examining the roles and relationships of settlement

1

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. patterns, increasing sedentism, agricultural intensification, and the

environmental context of site location (Custer 1986; Gardner 1986; Hantman

and Klein 1992; Kavanagh 1982, 1983r Potter 1993) but has not specifically

examined the continued role of animal procurement during these fundamental

shifts in the societies involved.

Although broad hypotheses have been made about the animals being

hunted and the relative importance of various species at various points in time

(Gardner 1986:88-89; Kavanagh 1982:70, 74, 79), more detailed aspects of

these statements have not been directly examined for Piedmont sites with in-

depth zooarchaeological analyses. Zooarchaeological analyses from sites in

the Late Woodland period have been performed on sites in the Coastal Plain

and have been incorporated into broader interpretations (Potter 1993; Waselkov

1982) and at least one study has been done in the Shenandoah Valley (Otter

1989) but, given the environmental differences between the physiographic

provinces and the possibility of differing external cultural contacts and

influences as well as in situ cultural developments, the interpretations resulting

from these analyses cannot be used to describe and interpret activities at sites

in the Piedmont. The current research examines the role of animal

procurement in prehistoric economies of the Potomac Piedmont by analyzing

the animal remains from six sites representing two distinct prehistoric

archaeological cultures and posits possible reasons for differences in animal

procurement strategies between these two cultures. These reasons include, but

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. are not limited to, differences in sedentism, reliance on food production, and

sociocultural complexity.

Background

In general, there are two basic types of plant food producing economies -

horticultural and agricultural. The difference between these is critical. As I am

defining them for this research, horticultural economies are determined as

containing strategies where people are deliberately planting and harvesting

plant foods, are depending on these foods as a predictable source of calories,

but yet continue following the previously developed seasonal round of

procurement activities with minimal change in procurement strategy. In this

definition, although it is possible that the result of the activities (the predictable

and reliable source of food) can have a dramatic impact on the society, planting

and harvesting activities themselves can be incorporated without major change

in the scheduling of other activities in the society.

In agricultural economies, in contrast, people are deliberately planting,

tending, protecting, and harvesting plant foods, are depending on these foods

as a predictable source of calories, and, as cultivation becomes the primary

subsistence strategy, must alter other parts of their culture to accommodate that

production. Agriculture is not the causal factor for culture change, but change

is effected when a commitment has been made 1) to invest time and energy

into an activity; and 2) to depend on the foods resulting from that activity to the

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. extent that it interferes with previously developed activities. This commitment

must be supported by or accompanied by other attributes of the culture. These

attributes may include having a part of the population who is responsible for

tending and protecting the crop throughout the growing season; having the

means to store and protect; having access to surplus goods for future use or

trade; and having at least a semi-permanent base camp or village near the area

where crops are being grown.

This definition of agriculture implies a certain degree of sedentism - one

where at least part of the population is occupying the same site year-round.

Although these sites can change locations, they are tied to the more productive

food-producing areas. While horticultural societies can also be relatively

sedentary, the main difference here is that sedentism with horticultural societies

is possible but not required. On the other hand, with agricultural societies, a

certain degree of sedentism is required to support the year-round involvement

with food production.

Given this definition, the increasing time and labor demands of

agricultural production necessitate prioritizing other activities and reallocating

remaining time and labor accordingly. Hunting, as a continuing critical source

of food, certainly remains important in the economies under examination but the

strategies used and the time and labor allocated to perform hunting activities

could have changed drastically.

Determining the difference between horticultural and agricultural

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. economies archaeologically is not always easy nor even always possible. This

is especially so since societies change on a continuum and not necessarily with

dramatic shifts that might leave easily recognizable archaeological evidence as

a group moves from horticulture to agriculture. Therefore, if examining the

evidence of changes in hunting strategies can be used to determine these

differences, then the current research will contribute to this discussion. As will

be discussed in more detail below, these possible changes in hunting strategies

are numerous and can vary greatly between cultures.

There have been many theories concerning the causes of the

development of agriculture and the rate at which cultivation in general became

economically critical after its initial development. These causes include

environmental determinism, opportunity and convenience, regional exchange of

plants and animals, population pressure, and a combination of all of the above.

Finally, while we may never completely understand why agriculture developed

in a given area, we are reaching a point in data collection when we can more

fully examine the process by which it happened.

One of the earliest theories on the origins of agriculture was proposed by

V. Gordon Childe in 1951 when he stated that "The period when the food-

producing economy became established was one of climatic crises adversely

affecting precisely that zone of arid sub-tropical countries where the earliest

farmers appear, and where the wild ancestors of cultivated cereals and

domestic animals actually lived" (Childe 1951 in Streuver (editor) 1971:15).

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 6

Although the proximity and availability of plants and animals conducive to

domestication were necessary, in this environmentally deterministic model it

was climatic change that provided the impetus to actually domesticate these

and incorporate them into a food producing economy.

Braidwood disagreed with these causes for food-production and instead

put forth the idea that "The food-producing revolution seems to have occurred

as the culmination of the ever increasing cultural differentiation and

specialization of human communities” (Braidwood 1960:6). Domestication of

both plants and animals was a step in the progression of cultural evolution as

humans became increasingly familiar with their environment and the plants and

animals around them. As independent cultures reached the required level of

complexity, the development of agriculture and animal husbandry occurred and

then was diffused throughout the world from those centers of development

(Braidwood 1960:6).

Binford (1968) in his early work, saw adaptation as a local problem, with

selective pressures resulting from conditions of non-equilibrium in the

ecosystem. The development of cultivation occurred in systems where three

basic conditions occurred: sedentism; population growth; and an increase in

potentially hostile contact between neighboring groups as populations

expanded. These three conditions produced increasing pressure upon the local

environment, the result being strong selective pressure for the development of

more effective and efficient means of food production.

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Flannery (1969), in a discussion on the origins of agriculture in the Near

East, concluded that intensive food production was due to "a series of

responses to disturbances of density equilibrium in human populations around

the margins of favoured areas, caused by the fact that those areas were the

zones of population growth and emigration" (Flannery 1969 reprinted in

Streuver 1971:78). While the major goal of the development of farming was a

stable food supply, other results of this development included 1) a change the

means of production, 2) the development of a division of labor, 3) the

stimulation of social stratification, and 4) an increase in environmental

degradation so that even if humans wanted to return to their previous

exploitation patterns it would not have been possible to do so (Flannery 1969

reprinted in Streuver 1971:78). Not only were plants and animals native to

certain ecological zones domesticated, but as people moved between these

zones, plants and animals were brought with them where they were not only

protected, but selected for propagation.

Boserup (1965) proposed that population pressure was the required

impetus for the development of agriculture. In this discussion, the optimal

carrying capacity (the largest population size that can be supported by

available resources in a given area) is a critical variable. As populations grow

past this optimal carrying capacity, they must develop ways of producing more

food. Without this pressure on the environment, the need to produce more food

than was already available would not be present. The development of

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. agriculture is not the only way that cultures can increase their access to food.

Cohen (1977), for example, sees an increasing reliance on marine resources as

a response to population pressure. Although the various degrees of food

production between the hunting and gathering of wild resources and the

development of agricultural production may vary among cultures, Boserup, as

well as many others, felt that population growth was a requirement for food

production to occur.

Regardless of the causes of the development of agriculture, it is clear

that at different points in time, many cultures around the world independently

domesticated plant resources and eventually became dependent on them to

some degree. This process was not accomplished quickly; indeed, as is shown

in a recent volume on the origins of agriculture (Cowan and Watson 1992), in

many areas of the world this process took thousands of years. In Eastern

North America, the initial domestication of the indigenous seed plants

sumpweed (Iva annua), sunflower (Helianthus annuus), and goosefoot

(Chenopodium berlandieri) occurred between 2050-1050 B.C (Smith 1992:106).

A domesticated variety of squash (Cucurbita pepo ) was present after 1050 B.C.

but there is no evidence that it was present in the area prior to that time. It is

also not yet clear whether the C. pepo present after 1050 B.C. was introduced

or was domesticated from an indigenous wild progenitor.

The earliest evidence of maize in the Eastern Woodlands is from an

AMS date of A.D. 175 + 100 from the Icehouse Bottom site in eastern

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Tennessee (Chapman and Crites 1987 in Smith 1992). Although it is evident

from the archaeological record that maize was increasingly cultivated, it did not,

however, become a staple food until after A.D. 1100 (Smith 1992:110-111).

This reliance on maize, as well as the cultivation of beans ( Phaseolus vulgaris)

and the previously mentioned plants, developed along various trajectories

throughout the Eastern Woodlands in combination with a continued reliance on

wild plants and animals. Since there were at least four plant species

domesticated prior to the introduction of maize - squash ( Cucurbita ), sumpweed

(Iva annua), sunflower (Helianthus annuus), and goosefoot ( Chenopodium

berlandieri ) - there was already an established behavior of cultivating plants that

could be readily adapted to the cultivation of maize. The domestication of these

plants does not mean that the people domesticating them were dependent on

them for predictable food. Indeed, Smith maintains that seeds from these

plants are relatively rare in the early archaeological record and food production

did not play a significant economic role in the region until 550-50 B.C. (Smith

1992:107-108). Agriculture in this area was not then a dramatic change in the

economy brought about by the appearance of domesticated species, but rather

"The maize-centered food production systems of late prehistoric groups in the

East can thus best be viewed as largely compatible extensions of pre-existing,

long-evolving subsistence systems" (Smith 1992:113-114).

The role of hunting strategies within food-producing economies has

become a growing topic of archaeological research. In particular, garden

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hunting, a theory that postulates that with the intensification of agriculture

people will exploit certain species that frequent borders of fields, has become

increasingly addressed in the archaeological literature (Kent 1989; Linares

1976; Neusius 1990; Speth and Scott 1989; Szuter and Bayham 1989). Linares

(1976), in the defining piece on garden hunting, found at the site of Cerro Brujo

in Panama that the faunal assemblage had three major components. The first

component indicates a focus on the collared peccary, a species that is relatively

peaceful, needs a small territory, is used to disturbed conditions, and readily

eats cultivated crops. The second component indicates a focus on the white­

tailed deer, which can withstand heavy harvesting and subsists in open brush,

grassland, and disturbed areas, especially those with cultivated crops, instead

of the brocket deer which is solitary and lives in more forested areas. The third

component indicates a disproportionately high hunting of the small rodents,

agouti and paca, relative to their natural biomass, species which also eat

cultivated plants (Linares 1976:346-347). Together, these three components

add up to a model where hunting is focussed on both large and small animals

that can be found in the gardens and immediately surrounding border areas.

An alternative model of adaptation in a context of increasingly limited

resources is known as the diet breadth model. The diet breadth model states

that as a particular resource (i.e., a species) becomes depleted as a result of

localized overhunting, lower ranked species will be hunted instead of increasing

the costs to search and hunt favored resources. Speth and Scott (1989)

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critically address both the diet breadth and garden hunting models. Through an

examination of the archaeological literature of the American Southwest and

ethnographic literature on contemporary horticultural societies, they found that

as some societies become more heavily committed to food-production rather

than becoming increasingly dependent on small mammals there were many

cases where the ratio of large to small mammals increased as people were

engaged in high-risk high-energy consumptive behavior to acquire these large

mammals. They give several possible reasons for this willingness to invest

large amounts of time and energy to hunt one particular taxa. One of these

reasons is that by having a predictable high caloric yield from horticultural

activities, time and energy are available to engage in high-risk time-consuming

activities such as hunting large mammals over a broad territory. Another

reason is that local game sources may become depleted as a result of

continued localized hunting. Traveling longer distances to hunt large mammals

therefore becomes more productive than traveling the same distance to hunt

small mammals.

These differing views, garden hunting and long-range hunting, are not

presented here as mutually exclusive hunting strategies where one or the other

will always or even most frequently be the strategy used by horticultural

societies. Rather, these two strategies are just two of many possible strategy

options that can develop as a society becomes more committed to a food

producing economy and will vary in different environmental contexts. Two of

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these strategies, a focus on limited large mammals and small mammals as at

the Cerro Brujo site (Linares 1976) and traveling long distances to hunt large

mammals (Speth and Scott 1989), were outlined above. However, it is also

possible that a combination of these two strategies could be used. Although

the discussions above were the result of research with horticultural societies, it

is possible that these strategies could be used by agricultural societies. The

current examination of Late Woodland Potomac Valley sites will contribute to

this discussion of changing hunting strategies.

The discussion of garden hunting can be used not only to address issues

of strategies of resource procurement but can also question the traditional view

of male hunters as providing the bulk of animal resources. Opportune hunting

while tending a garden would imply that men were not the only hunters in a

society unless men were the only people tending gardens. If women, children,

and the elderly were tending gardens, they would be just as likely to be

contributing to the animal resources that were collected. While the current

examination of hunting strategies will not provide direct evidence for gender- or

age-specific participation in hunting activities, the implications of it as indirect

evidence will be examined.

Test Implications

A systemic approach to the explanation of cultural change posits a

relationship of close interaction among all aspects of a given cultural system.

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This approach does not suggest that any one of these features plays a

deterministic role but acknowledges that all aspects of any society, from

environmental context to ideology, play important roles in the overall definition

or description of that society. This context of interrelatedness allows one to

postulate that, given a shift to an increased reliance on food production and a

more sedentary lifeway, there may be concurrent shifts in strategies of animal

resource procurement. While there are probably changes in other aspects of

the cultural systems as well, the data analyzed here will not necessarily be able

to address those changes directly.

There are at least three ways in which these shifts in animal

procurement strategies could be manifested:

► One, there could be a concentration in the use of certain animal

species mirroring the concentration in the use of certain cultivated plant

species. One possible example of this could be a use of only more productive

animals - animals with a relatively large amount of meat provided for the energy

invested in hunting. If more time and energy is invested in agricultural related

activities and less time is available for hunting then a decision could be made to

maximize that hunting time by focussing on the most productive resources.

► Two, there could be a complete restructuring and rescheduling (in

both species hunted and season of the year when hunted) of the exploitation of

available animal resources. Again, if there are increasing demands on time and

labor because of agriculturally-related activities, then a variety of changes in

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hunting strategies could occur. These could range from investing the available

hunting time in collecting a few highly productive species, as described above,

to collecting all available species within the surrounding area, to hunting only

the easily accessible animals - those animals either found feeding in the

gardens or that take a relatively small amount of time to hunt. Some key

agricultural activities such as planting and harvesting are seasonal and the

seasonal availability (or lack thereof) of time for hunting could affect the time of

year when more hunting is performed.

► Three, there could be no evident change in hunting and collecting

strategies. This could indicate that the initial strategies were so successful that

either they could be adapted fairly readily to new situations with a minimum of

change or that the increase in cultivation activities did not affect the time and

energy needed for hunting.

Goals and Objectives

The primary research goal is to examine animal based procurement

strategies over a ca. 600 year span of time during the Late Woodland period in

the context of relatively sedentary food producing economies; to interpret not

only the strategies evident at each site but how these change over time; and to

postulate possible reasons for these changes. Analysis of faunal assemblages

from six sites located in the Potomac and Monocacy River Valleys (Figure 1)

will be used to define these strategies.

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C olu m b ia

M a ryla n d F ig u re 1 istrict of S tu d y Area 18FR38 - Devubiss Bridge + 18FR14 - Biggs Ford 618FR18 — Rosenstock ®18M03 - Shepard gH-18M04 - Shepard Barrack Hughe§t®18M09 - Winslow

18M01 V irgin ia Pennsylvania 4-18AG43 — Moore Village 44PA1 - Keyser Farm West V irg in ia Mney-4 Quicksburg Bowman^' 0 Montgomery Complex Sites -)- Luray Focus Sites 0 0 Miles 10

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As described in the background information, other researchers have

noted a relationship between sedentism, increased emphasis on localized

resources, and maximization of resource security as providing a context for

examining the broader issue of the continuation and intensification of food

production strategies. Three possible alternative shifts in hunting strategies

which incorporate this relationship have been outlined above. Determining

which, if any, of these three shifts actually occurred will help to more clearly

understand this relationship.

The collection of sites analyzed for this research (Figure 1) span what

could be a 600 year period from ca. A.D. 900 to ca. A.D. 1500 (Figure 2) (Table

1). The earlier Montgomery Complex is represented by the Winslow (18M09),

Shepard (18M03), and Rosenstock (18FR18) sites. The later Luray Focus is

represented by the Keyser Farm (44PA1), Shepard Barracks (18M04), and

Hughes (18M01) sites. This collection of sites spans the period discussed

earlier during which food production was established throughout the region.

Although the faunal assemblages from all six sites were examined, the

assemblages from the Hughes and Rosenstock sites represent the two most

complete and most systematically collected assemblages, assemblages that

can be reliably used for describing and interpreting the hunting strategies used

by the people occupying these sites (see Chapter Three for a discussion of all

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. I KeyserI Farm j Quickstjurg j I M ile y | Bowman \/sjiepard Barrack stock V H u g h e s Moore Village s \ V H ughes^/ VRosenstock" /\Hughes ^Y lloore Village Ford VKosenstoek Sosenatock \ /^Rosenstoc Luray Focus X Xfiiggs xRosenstock v / / ' y\Shepari v v XRosenstoek XWinslow 1050 1100 1150 1200 1250 1300 1350 1400 1450 1500 1550 1600 1650 /(BigS3 Ford ' v ^She|ard ' j r XKosenstock v x ' ' Complex and Luray Focus Sites v lOoi lOoi Montgomery Complex v&2SSS~k ______

a Distribution of Dates for Montgomery 2 S hepard N / c t , V Win3low / VDevilbiss V/ Vwinslow F ig u re A.D. A.D. 800 850' 80(i 05^

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TABLE 1

RADIOCARBON DATES FROM MONTGOMERY COMPLEX, MASON ISLAND COMPLEX, AND LURAY FOCUS SITES

Site and Uncorrected Date B.C./A.D. Reference Sample No. Before Present

Montgomery Complex Biggs Ford (18FR14) SI-3661 915 ± 6 0 A.D. 1035 Stuckenrath, 1979 Kavanagh 1982:71 Rosenstock (18FR18) SI-4577 115 ± 75 A.D. 1835 Stuckenrath, 1980 SI-4578 530 + 60 A.D. 1420 Stuckenrath, 1980 SI-4579 615 ± 6 0 A.D. 1335 Stuckenrath, 1980 SI-4580 475 + 60 A.D. 1475 Stuckenrath, 1980 SI-4581 500 ± 30 A.D. 1450 Stuckenrath, 1980 SI-4582 935 ± 60 A.D. 1015 Stuckenrath, 1980 Beta-51754 910 ±90 A.D. 1040 Curry, pers.comm. Beta-51755 850 +120 A.D. 1100 Curry, pers.comm. Beta-51756 860 + 80 A.D. 1090 Curry, pers.comm. Beta-55044 520 + 80 A.D. 1430 Curry, pers.comm. Beta-55045 380 + 70 A.D. 1570 Curry, pers.comm. Beta-55047 700 ± 90 A.D. 1250 Curry, pers.comm. Beta-55048 720 + 70 A.D. 1230 Curry, pers.comm. Beta-55786 740 + 80 A.D. 1210 Curry, pers.comm.

Devilbiss Bridge (18FR38) SI-2898 845 ± 85 A.D. 1105 Stuckenrath, 1978 Kavanagh 1982:71

Shepard (18M03) SI-257 320 ± 240 A.D. 1630 Long & Mielke, 1967 SI-258 1060 + 280 A.D. 890 Long & Mielke, 1967 SI-259 1630 ±280 A.D. 320 Stuckenrath & Mielke, 1970 SI-553 730 + 60 A.D. 1220 Stuckenrath & Mielke,1970 SI-554 750 + 50 A.D. 1200 Stuckenrath & Mielke, 1970

Winslow (18M09) M-1189 1125 ±75 A.D. 825 Crane & Griffin, 1963 SI-37 635 ± 80 A.D. 1315 Sigalove & Long, 1964 SI-41 665 ±100 A.D. 1285 Sigalove & Long, 1964

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TABLE 1

Continued

Site and Uncorrected Date B.C./A.D. Reference Sample No. B.P.

Mason Island Complex Biggs Ford (18FR18) SI-3662 550 ± 9 0 A.D. 1400 Stuckenrath, 1979 Kavanagh 1982:77

Nolands Ferry (18FR17) Sl-3880a 875 + 65 A.D. 1075 Stuckenrath, 1978 Sl-3880b 745 + 60 A.D. 1205 Stuckenrath, 1978 SI-3880C 470 + 85 A.D. 1480 Stuckenrath, 1978 SI-3881 360 ± 60 A.D. 1590 Stuckenrath, 1978 Sl-3882a 455 + 60 A.D. 1495 Stuckenrath, 1978 Sl-3882b 1080 + 65 A.D. 870 Stuckenrath, 1978 SI-3883 1465 + 70 A.D. 485 Stuckenrath, 1978 Sl-3884a 400 + 60 A.D. 1550 Stuckenrath, 1978 Sl-3884b 855 ± 70 A.D. 1095 Stuckenrath, 1978 SI-3885 2200 ± 75 250 B.C. (?) Stuckenrath, 1978

Luray Focus Moore Village (18AG43) Beta-6782 200 ±50 A.D. 1750 Pousson 1983:148 Beta-6783 530 ± 50 A.D. 1420 Pousson 1983:148 Beta-6784 450 ± 5 0 A.D. 1500 Pousson 1983:148 DIC-2639 550 + 70 A.D. 1400 Pousson 1983:148

Biggs Ford (18FR14) SI-3663 765 + 70 A.D. 1185 Kavanagh 1982:79

Hughes (18M01) Beta-41367 660 ± 50 A.D. 1290 Dent & Jirikowic, 1990 Beta-41368 510 ±50 A.D. 1440 Dent & Jirikowic, 1990 Beta-49132 420 ±60 A.D. 1530 Dent, pers.comm. Beta-49133 580 ± 60 A.D. 1370 Dent, pers.comm.

Shepard Barrack (18M04) Sl-44 430 ± 70 A.D. 1520 Sigalove & Long, 1964

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assemblages). There have been 13 radiocarbon dates taken from the

Rosenstock site (Curry 1993), and they range from 935 + 60 B.P. (SI-4582)

(A.D. 1015) to 380 ± 70 B.P. (Beta-55045) (A.D. 1570) with the median of dates

in the late 13th century. Radiocarbon dates from the Hughes site are 660 + 50

B.P. (Beta-41367) (A.D. 1290), 510 ± 50 B.P. (Beta-41368) (A.D. 1440) (Dent

and Jirikowic 1990:73), 420 ± 60 B.P. (Beta-49132) (A.D. 1530), and 580 ± 60

B.P. (Beta-49133) (A.D. 1370) (Dent 1993, personal communication) (see Table

1 for citation of relevant radiocarbon dates). As these dates indicate, the time

span between these two sites ranges from 100 to 300 years. While there is

some overlap in the ranges of dates for these two sites, in general the dates

from Rosenstock and the other Montgomery Focus sites cluster approximately

300 years earlier than the dates from Hughes and the other Luray Focus sites.

Examining the animal remains from these two sites provides a unique vantage

point from which to discuss the relationship between sedentism, food

production, socioeconomic complexity, and hunting strategies and how changes

in these are reflected in and can be interpreted by the zooarchaeological

record.

Although the sites under examination in this research are commonly

referred to in the literature as being from agricultural societies, rarely is the term

agriculture defined in these statements. All of these sites are villages, and

although not explicitly stated in any of the discussions of these sites, it appears

that they were called agricultural because corn was present. However,

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according to the present definition of agriculture, this criterion alone is not

sufficient to designate an agricultural economy. Using the definitions developed

above, the presence of domesticated plants is the first prerequisite for

agriculture but it must be accompanied by year-round occupancy, a degree of

dependency upon those cultivated goods, and a changing of previously

developed activities to support and be supported by food-producing activities.

The relevant site data that will be used to help determine whether or not each

of these villages was agricultural will be presented in Chapter Two. The

analysis of the zooarchaeological data will be of primary importance in making

this determination but will necessarily need to be discussed in a context of

other site information. Further discussion, interpretation, and implications of this

determination will be discussed in Chapter Six.

Methodology

The methodology employed herein is designed to examine the changes

that were being made in the pattern of overall strategies of resource

procurement by focussing on faunal remains. I have placed the assemblages

that will be analyzed into two categories: primary and secondary. Primary

assemblages are those from sites which have been excavated more recently,

have accompanying detailed site information and interpretations (cultural

contextual information as well as physical site descriptive information), and

were collected in a relatively systematic fashion. There are two primary

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assemblages considered in this study - the Rosenstock site and the Hughes

site. Secondary assemblages are those which were excavated when the

collection of faunal remains was not of primary research importance or where

there is little other available site information. There are four secondary

assemblages - the Shepard site, the Winslow site, the Shepard Barracks site,

and the Keyser Farm site.

The secondary assemblages are currently being curated at the

Smithsonian Institution in the National Museum of Natural History (NMNH). The

analysis of these remains was performed by the author in the Smithsonian

Institution, Laboratory of Archaeobiology located at the Museum Support Center

in Suitland, Maryland. One assemblage, that from the Rosenstock site, was on

loan from the Maryland Historical Trust and was also analyzed at the

Archaeobiology Laboratory. The deer remains in the 1990 Hughes site

assemblage were analyzed in the archaeology laboratory at The American

University using a comparative specimen on loan from the NMNH

Archaeobiology Laboratory. Remains from species other than deer from the

1990 assemblage and the entire 1991 faunal assemblage from the Hughes site

were taken to the Archaeobiology Laboratory for identification using the

comparative collection located there. In addition, fish and bird remains not

identified using the comparative collection at the Archaeobiology Laboratory

were identified by Justin Lev-Tov at the University of Tennessee (U.T.) in

Knoxville using the U.T. comparative collection. The zooarchaeological

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methods used to collect all data are discussed in detail in Chapter Four. The

data recovered from all analyses were coded for entry into a dBASE 111+

database, and statistical summaries result from the manipulation of that

database.

This research provides interpretations from the archaeological record

through its use of existing collections, encouraging the conservation of

archaeological sites and further research on previously collected assemblages.

Four of the assemblages used in this research are from collections that have

been curated at the National Museum of Natural History for up to forty years.

Given the current rapid rate of site destruction and the non-renewable nature of

archaeological resources, techniques to obtain more information from curated

materials must be explored to insure that the optimum data is obtained from the

assemblages. This study illustrates the importance of using existing collections

to answer a variety of research questions. Criteria to evaluate the utility of

these curated assemblages for various types of research have been developed.

These criteria consist of a series of measures that can be taken on an

assemblage to determine what type of research the assemblage is best suited

for. Is an assemblage relatively complete (through both field collection and

curation methods) so it can be considered a representative sample of the

results of all animal use practices, or does this assemblage consist primarily of

bone tools so that it would be appropriate for a study of bone tool technology

and manufacturing techniques but with little usefulness for subsistence

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research? By determining the nature and the research utility of the

assemblages being examined, this research provides other archaeologists in

the region with descriptive assemblage data that can be used when designing

additional research questions that can be addressed with these assemblages.

Analyses of all these data will allow me to construct overall descriptions

of subsistence strategies. These analyses include species and element

identification, season of procurement, and population demographics

(specifically, sex and age of individual animals at death). This information can

be used to determine which, if any, of the three possible shifts in resource

procurement strategy discussed above was occurring. The presence of species

concentrations can be illustrated primarily by species representation and

species diversity, combined with seasonality information for the acquisition of

the animals. A shift in overall strategies can also be indicated primarily through

species identification and seasonality of hunting and can also incorporate the

demographic (sex and age) information.

Organization

There are five chapters following in this study. Chapter Two, "Culture

History," presents a brief culture history of the Late Woodland Period in the

Potomac Valley. It is organized chronologically and is followed by a discussion

of issues important to understanding cultural developments in the area. More

specifically, it discusses in detail the six sites analyzed for this research and

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places them in the broader cultural historical framework for this area and time.

Chapter Three, "Assemblage Recovery and Utility," examines the varying

excavation and recovery techniques used at each site examined in this

research. Using this information in conjunction with some basic descriptive

measures on the faunal assemblage, the research utility of each assemblage is

then examined. In this chapter, it will be determined how relatively complete a

sample each faunal assemblage is of the archaeological record and to what

degree each assemblage can be accurately used to address the current

research. For example, if a faunal assemblage consists primarily of bone tools

at a site known for having yielded several thousand faunal specimens, then it

can be concluded that this assemblage is not appropriate for a subsistence

study.

Chapter Four, "Analytical Methods," presents the sampling strategies

used for each assemblage, the zooarchaeological methods used in analyzing

the faunal material, and the coding system developed for recording all data.

Because the size of the assemblages varied greatly, a sampling strategy was

designed for each site assemblage. A description and justification of each

sampling strategy will be discussed. Zooarchaeological methods discussed

include the specific information that was collected for each specimen, how that

information was collected, and the equipment used during analysis. In addition,

the criteria used for aging and sexing specimens and the observations and

measurements taken to address these criteria will be discussed. Finally, each

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statistical test used in the later interpretation of the data is defined and its

relevance to the current research is discussed.

Chapter Five, "Summary of Data," presents summaries of the data

collected in the analysis of the faunal assemblages. Many of these are in

simple tables of numbers and percentages of various information such as the

number of taxa identified in each assemblage, the element distribution for

chosen taxa, the number of specimens of each taxa, etc. In addition,

descriptive and statistical data needed to address specific questions such as

seasonality, off-site animal processing, butchering activities, and taxa selection

during hunting are presented. These data are organized by archaeological

culture and then by site. This was done to facilitate comparisons of the two

cultures, the Montgomery Complex and the Luray Focus, as well as

comparisons between sites within these two cultures.

Chapter Six, "Conclusions," concludes this study. In this chapter, the

initial research questions discussed in Chapter One are addressed using the

data collected and presented throughout the rest of the text. Implications of the

results are discussed and directions for future research are presented. More

specifically, the use of curated collections will be addressed and other

appropriate uses for these specific faunal assemblages will be discussed.

Conclusion

In conclusion, there has been much discussion in the archaeological

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literature regarding the relationship between food production, sedentism, and

the role of animal resources in increasingly complex societies. Much of this

research has been performed in areas where a variety of animals were

becoming domesticated and were therefore becoming one of the more

predictable and reliable food resources.- It is only in the last two decades that

this research has been extended to include situations where animals were not

domesticated but nonetheless played an important dietary role. This

discussion, however, has largely been ignored in the Middle Atlantic region of

the Eastern Woodlands, partly because of a lack of large systematically

collected zooarchaeological assemblages and partly because of the need to

examine other questions about cultural change and adaptation in the region.

The present research uses animal remains from archaeological sites in this

region to examine animal resource procurement strategies in a context of

increased sedentism, intensification of plant food production, and increasing

socioeconomic complexity and will highlight key aspects of economic change in

local prehistory.

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. CHAPTER 2

CULTURE HISTORY

Introduction

The questions addressed with this research examine animal resource

procurement and utilization strategies and the relationship between these

strategies and a series of socioeconomic changes that were occurring during

the Late Woodland prehistoric period in the Middle Potomac River Valley. The

Late Woodland period in the Potomac Valley Piedmont is typically separated

into three archaeological cultures that overlap slightly both temporally and

geographically. Chronologically, these cultures are the Montgomery Complex,

the Mason Island Complex, and the Luray Focus, also referred to as the Keyser

Complex (Clark 1980; Kavanagh 1982; McNett 1975) (Table 1). Two other

archaeological groups adjacent to the study area which are important to an

understanding of the Late Woodland period in the Piedmont and that will be

described later in this chapter are Shenk's Ferry and Monongahela, located

primarily in Pennsylvania.

The six sites yielding assemblages for this research were occupied from

circa A.D. 900 to circa A.D. 1530. Although only two of the three Potomac

28

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Piedmont cultures, the Montgomery Complex and the Luray Focus, are

represented by these six sites, all three will be described to provide a more

detailed and complete interpretation of the progression of social and economic

traits and their changes over time. The two cultures that are represented by

assemblages in this study are the Montgomery Complex (represented by the

Shepard site, the Rosenstock site, and the Winslow site) and the Luray Focus

(represented by the Hughes site, the Shepard Barrack site, and the Keyser

Farm site). In general, the Mason Island Complex is not as well understood as

the Montgomery Complex and the Luray Focus. Therefore, interpretations and

discussions of the Mason Island Complex presented here will not be as detailed

as those for the Montgomery Complex and the Luray Focus.

There are several key elements which are used here to distinguish and

define these archaeological cultures. These elements include geographic and

time range; descriptions of artifact assemblages including ceramics, lithics, and

bone tools; internal site organization as reflected in the size and layout of

features; mortuary patterns; and subsistence patterns. These variables will be

described for each complex with examples provided either from sites analyzed

in this study and/or sites that are considered representative of the complex.

Montgomery Complex

The Montgomery Complex marks the beginning of the Late Woodland

period in the Potomac Piedmont and ranges in time primarily from circa A.D.

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 900 to circa A.D. 1300 (Clark 1980) (Table 1). Although some of the

radiocarbon dates from this complex fall either before A.D. 900 or after A.D.

1300, some of these dates, such as the A.D. 1835 date from Rosenstock and

the A.D. 320 and A.D. 1630 dates from Shepard are obviously far out of the

normal range for these assemblages and must be considered unreliable. The

remaining four post-A.D. 1300 dates for this complex are all fifteenth century

dates from Rosenstock. These dates could indicate some later occupation at

this site, however the majority of the dates from this site fall within the A.D. 900

- A.D. 1300 range and indicate that the primary occupation of this site is during

this time frame.

The Montgomery Complex was labeled by Slattery when he originally

distinguished it from the later Luray Focus (1952:62). This early definition was

expanded by Tidwell (1967) incorporating material from the Winslow site, the

Fisher site, the Kern site, and the Shepard site. Slattery and Woodward (1992)

provide additional analysis of the artifact assemblages from these sites to give

a more detailed description of the various traits considered central to the

Montgomery Focus. McNett (1975) later renamed the Montgomery Focus the

Montgomery Complex based on a review of Potomac Valley archaeology and

an evaluation of the available literature.

Excavations at and interpretations of the Rosenstock site provide

additional data with the potential to both expand and refine definitions and

descriptions of the Montgomery Complex. While the Rosenstock site has

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undergone extensive excavations in the past few years, the artifacts have not

yet been completely analyzed. As a result, discussions and conclusions about

the Rosenstock non-faunal material can be only preliminary at this point. In

addition, results from test excavations at and examination of a surface collection

from the Devilbiss site and excavations at the along the

Monocacy may be able to provide further detail on site structure and artifacts

from a broader geographic range of Montgomery Complex sites. Biggs Ford is

a multicomponent site, and dates from each component are listed separately in

Table 1 in their appropriate section.

Major sites in the Montgomery Complex typically consist of riverine-

oriented, generally oval shaped villages, one to two acres in size. Many are

associated with Huntington silty loam, a rich soil particularly well suited for food-

production. Although hunting and fishing remained critical in food production

and acquisition cycles, the increasing needs and impacts of a developing food-

producing system must have affected, and been affected by, other aspects of

this culture. It is the extent of these impacts on the hunting strategies that is

being addressed with this study and will be examined later.

Village Organization

A circular pattern of pits is one of the more prominent archaeological

traits at village sites in this complex. Although postmolds are abundant at all of

the sites, they do not appear to be in a distinguishable pattern that would

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indicate size and/or number of house structures present at any given point in

time. Some postmolds do appear to be in a circular pattern, and it is possible

that these represent individual dwellings. It is also possible that these dwellings

may be associated with both trash and/or storage pits.

The Winslow site exhibits the typical Montgomery Complex pattern of

pits. A total of thirty-three trash/storage pits were excavated. The main village

area contained a semi-circular pattern of frequently overlapping pits. Ranging

in size and depth from 32-60 inches in depth, they were generally ovoid or

elongated in plan view. Although several pits were located outside of the main

pit line, only six of these were not burial pits (Slattery and Woodward 1992:17).

MacCord, Slattery, and Schmitt comment that "The most notable feature

revealed in the excavations at the Shepard site was the profusion of pits" with

over eighty pits excavated (MacCord, Slattery, and Schmitt 1957:7). These

were random throughout the site and some were overlapping or abutted other

pits. Although some of the pits had originally been excavated for storage and

then later used as either trash pits or burials, the function of most of the pits

was indeterminable. The size of the pits that were measured ranged in

diameter from three to five feet and were up to five feet deep.

Ceramic Artifacts

The most frequently used defining trait for the complexes discussed here

is ceramic type. The Montgomery Complex is defined partially by the presence

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of the ceramic type known as Shepard Cord-Marked. This type was originally

included in Evans’ 1955 category of Albemarle wares (Evans 1955:39-44).

Shepard wares are made from a compact clayey paste tempered with crushed

rock, most frequently crushed decayed granite or quartz, and show complete,

well-controlled firing. The shape of these vessels is generally globular with

bases ranging from round to conical. The necks are constricted which bring the

opening of the vessels to almost the diameter of the widest part of the body

with rims straight to outflaring . Many Shepard ware rimsherds are folded or

contain a distinctive appliqued external collar.

Decoration of the outside of these vessels consists primarily of variations

of cord-marking and/or incising. Interiors of the vessels are smooth. Much of

the decoration is found on the collar. This decoration often consists of parallel

bands of cord impressions on the lips of the vessel with the base of the collar

frequently containing oblique cord-wrapped stick impressions and occasionally

oblique incising slanted in the opposite direction at the base of the rim

(MacCord, Slattery, and Schmitt 1957; McNett 1975; Tidwell 1967; Slattery and

Woodward 1992).

There was a variety of ceramics recovered from both the Shepard and

the Winslow sites. Some of these, such as the Selden Island steatite- and

sand-tempered ware and the steatite-tempered Marcey Creek ware recovered

at Winslow, were from an earlier occupation found underlying the primary

Montgomery Complex occupation. Other Late Woodland ceramics recovered at

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both sites include Page Cord-Marked, Chickahominy, Rappahannock Incised,

Keyser, Potomac Creek, and Clarksville. These minority wares were relatively

infrequent, and the majority of the sherds recovered from both sites were

Shepard Cord-Marked (Slattery and Woodward 1992:12-15, 28-51).

The most common ceramic type recovered at the Rosenstock site is

Shepard Cord-Marked. As stated earlier, this ware typically dates to

approximately A.D. 900 - A.D. 1300. Additional wares recovered include, in

descending order of frequency, Accokeek (Early Woodland, 800 B.C. to 300

B.C), Keyser (Late Woodland, A.D. 1450 to Contact), Page (Late Woodland,

A.D. 1300 to A.D. 1500), Marcey Creek (Early Woodland, 1200 B.C. to 900

B.C.), and Shenk's Ferry (Late Woodland, A.D. 1250 to A.D. 1550) (Curry and

Kavanagh 1992:27-31).

Lithic Artifacts

The formal flaked tools in the lithic assemblages from the Montgomery

Complex consist primarily of triangular projectile points made of rhyolite with

concave bases, quartzite, quartz, and chert, with occasional points made of

jasper. Additional flaked stone tools include preforms, blades or knives, drills,

and scrapers. Ground stone tools recovered consist of celts, hammerstones,

and both perforated and unperforated discoidals (Slattery and Woodward 1992).

In the Winslow site assemblage, flaked stone tools include projectile

points, blades/knives, drills, small end-scrapers, one large scraper, and one

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axe. The majority (87%) of the points are small and triangular in form. Ground

stone tools include one abrading stone and at least three celts. Other ground

stone artifacts include one unfinished pipe and 115 complete or fragmented

discoidals (Slattery and Woodward 1992:58-66).

Projectile points from the Shepard site are likewise primarily small and

triangular. Other flaked tools included drills, a knife, and scrapers. Ground

stone tools recovered included celts, one felsite axe, one chisel, hammerstones,

and one quartzite pestle. Other ground stone items included one sandstone

discoidal, one small fragment of a sandstone tablet, one partially perforated

chlorite spheroid, one slate bead, one fragment of a possible slate gorget, and

one possible unfinished chlorite bead (MacCord, Slattery, and Schmitt 1957:16-

19).

A variety of projectile points have been recovered from the Rosenstock

site. The majority of these are triangular, either Madison or Levanna types.

Madison points are the most frequently found and are the smaller of the two

types. Madison points "vary from nearly equilateral specimens to isosceles

triangles nearly twice as long as wide. Bases are either straight or concave.

The time range for the Madison is estimated at A.D. 1000 to Contact" (Curry

and Kavanagh 1992:32). For Levanna points, "Most are equilateral triangles,

with the rest described as broad isosceles triangles. Bases are usually

concave, although a minority have straight bases" (Curry and Kavanagh

1992:32). Levanna points in the area begin at approximately A.D. 700, become

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common at approximately A.D. 900, and by A.D. 1350 begin to be replaced by

Madison points. Other types recovered from this site include

Selby Bay which typically dated to the Middle Woodland period at

approximately A.D. 200 to A.D. 900 and are associated with Mockley ceramics,

and LeCroy projectile points, an Early to Middle Archaic point which has been

dated to 6300 ±100 B.C. (Broyles 1971). These possibly represent an earlier

occupation at this site. Other flaked stone tools recovered from the Rosenstock

site include stemmed and notched bifaces which could be either Late Archaic

projectile points or Late Woodland knives or multi-function tools. Ground stone

objects recovered include several small carved slate objects, celts, and a

portion of a stone bead.

Worked Bone and Antler Artifacts

Bone tools are numerous throughout Montgomery Complex sites. These

artifacts include awls, beamers, projectile points, fishhooks, cups, and scoops

or bowls constructed from turtle carapace. Although the presence and

abundance of bone tools from earlier excavations have been coded in this

research, these artifacts have not been specifically examined in great detail for

this study. As a result, most of the discussions of specific patterns of bone

tools have been extracted from previous research published on these sites.

The exceptions to this are the discussions using the material from the

Rosenstock site, the Shepard Barrack site, and the material from the later

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excavations at the Hughes site.

A wide variety of bone artifacts were recovered from the Winslow and

Shepard sites. These include: cut antler with the tines missing, presumably the

waste from antler projectile point manufacturing; antler tines, the majority of

which show either striations running parallel to the long axis of the antler or

wear from having been used as pressure flakers, or were ground into projectile

points; antler 'flakers,' presumably used for flaking during stone tool production;

awls; beads; chisels; fishhooks; 'beamers' made of metapodials from white­

tailed deer; and one small triangular piece of antler with a semi-circular beveled

hole across the base. In addition, several polished plastron and carapace

pieces were recovered, some of which had been perforated and most of which

showed wear across the edge (Slattery and Woodward 1992:67-75). Antler and

bone artifacts recovered at the Shepard site that were not recovered from the

Winslow site include antler cylinders of unknown use, antler celts and scrapers,

one bone needle, several bone pendants, and a bone scraper (MacCord,

Slattery, and Schmitt 1957:19-21).

Bone and antler tools recovered from the Rosenstock site include

beamers, awls, needles, and flaking tools. Other bone and antler artifacts

include beads, antier tines and shafts which show evidence of having been

scored and cut, and long bone fragments which are polished due to use wear.

A more detailed study of the bone tools is not available.

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Mortuary Patterns

Burials from sites in the Montgomery Complex are typically flexed

individual interments. At various sites, these burials are located both within and

without the circular pit line surrounding the central portion of the site. The

deliberate inclusion of grave goods varies, but artifacts recovered from this

context are most frequently found in children or infant burials and consist

primarily of shell and bone beads which appear to have been used for personal

adornment.

At the Winslow site, 15 complete or nearly complete burials were

recovered and, with one exception, were located outside the circle of refuse

pits. Ten of these burials were of adults, three were male and seven were

female. There were five infant burials of undetermined sex. All of the

skeletons were in a flexed position. None of these burials contained grave

goods.

At the Shepard site, a total of 33 human burials were exposed during all

excavations. While some of these were located within refuse pits, it appears

that the majority of them were located outside the semi-circular line of

refuse/storage pits described above. Eighteen of the burials were flexed, two

were bundled, and one was extended. Of the adult burials, six were male and

ten were female. All fifteen of the infants and children were of undetermined

sex. There are no available data for the remaining two individuals. Only nine

of the burials contained what was interpreted as deliberate grave goods

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(MacCord, Schmitt, and Slattery 1957:9-11; Slattery and Woodward 1992:133).

Of these nine burials, seven of them were infants, children, or sub-adults.

Since no other burials containing grave goods have been recovered from any of

the other sites from the Montgomery Complex, it is impossible to determine if

this trait of including grave goods primarily with children's burials was site

specific or if it occurred throughout the cultural complex. The sex, age, and

associated grave goods of these nine individuals is listed below in Table 2.

Subsistence Patterns

Existing descriptions of subsistence patterns for the Potomac Valley Late

Woodland period are general and consist mainly of broad statements that these

groups were horticultural or agricultural, hunted, and gathered local resources,

probably on an annual round of activities based on the seasonal availability of

both plants and animals. While this gives a broad idea of a mixed economy, it

does not give any detail with which to test the questions being asked in this

study. Direct evidence about subsistence patterns at all of the sites in this

study is limited primarily to the observance of domesticated plants such as corn

and beans and various wild nut shells and initial species list of animal taxa

present. No estimates of associated cultivated field sizes has been performed

nor have there been any estimates as to the proportions of domesticated versus

wild plants in the archaeobotanical assemblages.

To evaluate the subsistence patterns at the archaeological cultures under

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TABLE 2

BURIAL DATA FROM THE SHEPARD SITE (18M03) COMPILED FROM SLATTERY AND WOODWARD 1992 AND MACCORD, SCHMITT, AND SLATTERY 1957

Burial # Sex Age Associated Artifacts 1 ? 1 yr. 1 shell bead and 43 tubular shell beads

2 M 14-15 yrs. 100+ Marginella beads and one tubular bone bead

6 ? 4 yrs. 100+ miscellaneous shell beads

8 ? 6-7 yrs. knobbed bone flaker in right hand

9 ? 6 mos. shell beads

12 M 20 yrs. fragmentary stone gorget

14 ? 18 mos. shell disk beads

21 ? 6 yrs. 9 perforated oyster shells, 110 tubular bone beads, 32 squirrel mandibles, and 1 clam shell disk

33 F 20-25 yrs. 134 tubular bone beads, polished bone tube (length of 19.05 cm), 65 tubular shell beads, 400+ Marginella beads - all of these were near the head or arm appearing to the excavators that they were part of a hair decoration and bracelet

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study in this research, all known archaeobotanical evidence for the sites under

study will be presented. Because the results of the faunal analysis will be

presented in Chapter Five, broad summary statements of these results and of

faunal data known to date will be presented in this chapter. Detailed results,

their interpretations, and the implications of the data can be found in Chapters

Five and Six.

For sites from the Montgomery Complex, identified archaeobotanical

material consists of charred corn cob (Zea mays), corn kernels, and beans from

the Rosenstock site (Curry and Kavanagh 1991:2), hickory (Carya sp.), walnut

[Juglans sp.), and corn from the Winslow site (Slattery and Woodward 1992:75-

76) and corn and hickory (Carya glabra Mill ) from the Shepard site (MacCord,

Slattery, and Schmitt 1957:22). In addition, pit features attributable to the

Montgomery Complex at the Biggs Ford site contained "abundant" corn (Bastian

1974:5). While no further plant material was collected at the Shepard or

Winslow site, extensive flotation samples were collected at the Rosenstock site

and the future analysis of these will provide data directly relevant to the current

discussion in this study.

Faunal remains from the Montgomery Complex sites represent a wide

variety of animals. Various taxa in the assemblages were available at different

times of the year with the complete assemblages indicating year-round

occupation at these villages. Deer are the dominant taxa in the Montgomery

Complex assemblages with a wide variety of mammals, fish, reptiles, and birds

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being exploited. Although shell was evident at all of these sites, it has not been

fully analyzed to date. This data, combined with the archaeobotanical data

presented above, still leaves us with a very broad picture of subsistence

patterns known to date about the Montgomery Complex. This picture will be

refined below however when more detailed comparisons of the subsistence

patterns between the Montgomery Complex and the Luray Focus are

presented.

Mason Island Complex

Mason Island sites are archaeologically evident in the middle Potomac

Piedmont possibly as early as A.D. 1300, and certainly by A.D. 1400, appearing

to overlap slightly with both the Montgomery Complex and the later Luray

Focus. The Mason Island Complex ends at approximately A.D. 1500. Sites

originally used to define this complex include the Catoctin Creek site (44LD14)

excavated by McNett and Handsman, the Mason Island I site (44LD10), earlier

components at the Mason Island II site (44LD13), and the Glen Haven site

excavated by Ellis E. McDowell. Additional Mason Island sites excavated since

this definition include Biggs Ford (18FR14), Nolands Ferry (18FR17), Herman

Barton Village (18AG3), Jeffrey Village (44LD13), Claggett Retreat (18FR25),

and Point of Rocks (18FR8) (Kavanagh 1982; MacCord 1992).

The Mason Island sites listed above are primarily village sites located in

riverine areas, either associated with the Monocacy or the Potomac rivers.

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Sites in the Mason Island Complex are typically slightly upriver from

Montgomery Complex sites. Radiocarbon dates range from A.D. 870 (Sl-

3882b) to A.D. 1590 (SI-3881) at the Nolands Ferry site, a range overlapping

with but generally later than that of the Montgomery Complex sites. The Biggs

Ford site yielded one radiocarbon date from a Mason Island component. This

A.D. 1400 date (SI-3662) falls well within the range established at Nolands

Ferry. More clarification is needed for dating this complex, especially since this

date range overlaps with that from both the Luray Focus and the Montgomery

Focus. Though similar to the Montgomery Complex in some ways, differences

in the Mason Island Complex include ceramic temper, ceramic decoration and

burial treatment. These factors, combined with the temporal and geographic

variances were considered sufficient by McNett (1975) to merit these sites a

separate, albeit related cultural manifestation.

Village Organization

The internal organization of Mason Island sites is very similar to that at

Montgomery Complex sites. In general, these sites contain a circular array of

pit features, organized around what appears to be a central plaza area.

Ceramic Artifacts

Mason Island ceramics differ only slightly from those found at

Montgomery Complex sites. They are tempered primarily with limestone and

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occasionally with quartz and are referred to as Page Cord-Marked. Vessel

shape is similar to that found on Montgomery Complex sites, as is the presence

of cord-marking on the external surface of the body. Rim treatment varies over

time in this complex and includes straight, folded, and collared styles. Straight

rims appear early and are decorated with punch marks, either obliquely or with

a sideways "v" shape, or cord-wrapped stick designs. Later in the complex,

rims are typically folded. Collared rims range from earlier lens-shaped folded

ones which are decorated with gashes or punches on the termination or

occasionally are plain to a later applique rim which is either rectangular or

triangular in cross-section (McNett 1975).

Ceramics from the Catoctin Creek site, one of the major Mason Island

sites, fall into the two broad categories of Page and Shepard. While one of the

major differences between these two wares is that Page is usually tempered

with limestone and Shepard is usually tempered with crushed quartz, what

varies in more significant patterns is the range of decoration. When vessels are

sorted into groups based on decoration, temper is no longer such a meaningful

variable. Rim sherds with identical treatments were of both tempers, and

pottery at the site was categorized by collar decoration (McNett 1975).

Lithic Artifacts

Lithic tools from Mason Island sites consist primarily of triangular

projectile points made of quartz or rhyolite. The few other formal stone tool

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types that have been recovered include hammerstones, scrapers, celts, and

some tools which may have been used as hoes.

Worked Bone and Antler Artifacts

Bone and antler tools that were recovered from Mason Island Complex

sites include bone awls, fishhooks, flakers, projectile points, possible bone

handles, tubular bone beads, and beaver incisors used as chisels.

Mortuary Patterns

Burial treatment at Mason Island sites differs from those at Montgomery

Complex sites in some very basic ways. The first of these is that burials are

extended rather than flexed. Again, individual interments were the norm, but

some burials contained a flat slab above the body and others contained

ceramic vessels. In general, however, grave goods were personal decorative

items, usually in the form of Marginella and Columella beads (McNett 1975). It

is interesting to note that, as with the burials at the Montgomery Complex, it is

primarily infants and children who received grave goods.

Subsistence Patterns

Evidence for subsistence patterns being used at Mason Island sites is

scarce. Corn is present at most Mason Island sites as are charred wild nuts.

Detailed faunal analyses for Mason Island assemblages are not available.

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Because of this lack of data, little can be said about Mason Island subsistence

patterns except that they were most likely horticultural with the diet

supplemented by the collection of wild plants, nuts, berries and the hunting and

collection of both terrestrial and aquatic animals.

Lurav Focus

The Luray Focus, the last representative of the cultural developments in

the Piedmont to be discussed here, was first defined by Schmitt using data from

the Keyser Farm and the Hughes sites (1952:62-3). McNett (1975) later

included analyses from the Miley site (44SH2), the Bowman site, the Berryville

site, the Jones site, later levels of the Monocacy site (18FR100), and the later

component at the Mason Island II site (18M013). Finally, additional Luray

Focus sites include the Quicksburg site, the Moore Village site, the Cabin Run

Site, and the Shepard Barrack site.

Several cultural traits for this complex contrast sharply with those in the

preceding Montgomery and Mason Island Complexes, and some researchers

hypothesize that the Luray Focus may in fact be related to the Monongahela of

Western Pennsylvania (Manson, MacCord and Griffin 1944; MacCord and

Rodgers 1966; Schmitt 1952; Wright 1959; McNett 1975; Pousson 1983).

Indeed, the Moore Village is categorized by the principal investigator as a

"palisaded, Late Prehistoric, Monongahela village site" (Pousson 1983:xi) and

"that this [Monongahela] tradition in the upper Potomac is ancestral to that of

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the Luray Focus" (Pousson 1983:153). This relationship will be discussed in

further detail later. Radiocarbon dates from the Luray Focus range from A.D.

1185 (SI-3663) at Biggs Ford to A.D. 1530 (Beta-49132) at the Hughes site

(see Table 1). Two of the dates from the Moore village site, 200 B.P. (A.D.

1750) + 50 years (Beta-6782) and 450 B.P. (A.D. 1500) ± 50 years (Beta-

6784) are thought to be possibly contaminated and are therefore too recent to

be accurate reflections of the occupation of the site. This leaves the

occupation of this site somewhere around A.D. 1400. Two additional dates for

the Luray Focus include one date of A.D. 1640 + 120 (SI-136) and A.D. 1710 +

120 years (SI-136). With MASCA corrections, these dates become A.D. 1510-

1600 and A.D. 1630 (MacCord 1992:167).

Village Organization

The most striking difference between villages in the Luray Focus and

villages from earlier Piedmont complexes is that many Luray Focus villages are

palisaded. The patterning of the palisaded sites seems to consist of a series of

pits, including refuse pits, storage pits, and burial pits, and house structures

surrounding an open area. This pattern is not consistent for every Luray Focus

site. The Hughes site, for example, does not appear to be palisaded nor does

it have the open central plaza as originally thought after the initial excavations

in the 1930's observed by Stearns (Dent and Jirikowic 1990). Of the Luray

Focus sites mentioned above, the Miley site, the Quicksburg site, and the

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Moore Village site had conclusive evidence of a palisade. The remaining sites

either did not have a palisade or the postmold patterns were unclear and a

palisade or the outlines of structures could not be determined.

The majority of the pits which formed the main pattern at the Keyser

Farm site were circular in plan view and ranged in diameter from two to nine

feet. Other pits were either elliptical, pear-shaped, or irregular. In cross-

section, pits varied in shape and included hemispherical, straight-sided and

straight-bottomed, bell shaped, or combinations of all three shapes. Although

many of these pits overlapped, indicating that they were originally excavated at

different times, there appeared to be no difference in the artifacts recovered

from the overlapping pits. In addition, there were several storage/refuse pits

that were surrounded by postmolds. It is hypothesized that the postmolds

possibly represented either a roof-like structure over the pit or a fence to protect

it from scavengers (Manson, MacCord and Griffin 1944:379-386).

Clyde (1959), in the only published report for the Shepard Barrack site,

reports only one postmold and no other features for the limited excavations at

the site. This 1959 report briefly describes a 1958 and 1959 period of

excavation conducted by the Archaeological Society of Maryland (ASM). Given

the large quantities of artifacts and the scarcity of features that the ASM

reported, Clyde (1959) concludes that the site was not occupied for one

extended period of time but was probably revisited for short term use. In an

examination by E. Moore in December of 1992 of the Shepard Barrack artifacts

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in the NMNH collections, notes were found in the assemblage that referred to

certain artifacts being associated with five burials. No reference can be found

for these burials, and no record of them could be located in the accession

records at NMNH. Apparently additional testing and excavation may have been

performed at the site, but the results of that are unknown at this point.

Richard E. Stearns observed the excavations by Nicholas and Roy

Yinger at the Hughes site from 1937 to 1938, and descriptions of the early

excavations of this site come from a publication describing his observations,

accession records at the National Museum of Natural History, and notes

accessioned with the artifacts from this site. At least forty-two burials and over

135 storage/refuse pits were excavated at the Hughes site in the 1930's. At

least seven of these pits were surrounded by postmolds indicating some

structure associated with the pit. The majority of the pits were arranged in a

circular pattern with an open space on the north end of the circle measuring

approximately one hundred and twenty feet across. In addition, there was a

cluster of five burial pits containing seven individuals and two refuse pits in the

center of the village area. Because of the speed with which the Yinger brothers

excavated, Stearns was not able to observe postmold patterns at the site

(Stearns 1940).

The 1990 excavations at the Hughes site yielded 42 features. These

were divided into five categories; shallow, amorphous features; small basin­

shaped pits; large refuse pits; burials; and miscellaneous unclassified features

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(Dent and Jirikowic 1990:49). One hundred and sixty-eight postmolds were

recorded. Although no clear pattern was observed, these postmolds appeared

to occur in arcs across the site (Dent and Jirikowic 1990:55). The density of

postmolds throughout the excavated area limited the possibility of defining any

clear postmold patterns that would indicate structure size and shape. It is

probable that this density reflects repeated or long-term use of the area rather

than a single construction and occupation period. In addition, the five burials

and two trash pits observed in the center of the village during the earlier

excavations in combination with the ubiquity of postmolds across the site during

the 1990's excavations indicate that there was no completely open central plaza

as is hypothesized for other Luray Focus sites.

The organization of the Moore Village consisted of a plaza ringed by

houses which were surrounded by a palisade. This oval village measured circa

350 by 260 feet. Although no clear postmold patterns for houses or other

structures were discernible, there was daub present in some of the midden-

filled trench segments associated with the palisade (Pousson 1983:53). Daub

has not been observed at any of the other Luray Focus sites nor at any other

Monongahela sites. Pousson (1983:150) hypothesizes that since daub is only

preserved when it is burned, the paucity of daub at other related sites may be

due to disparate preservation rather than it not being used elsewhere. The clay

for the daub at the Moore Village site was most likely excavated from trenches

between the palisade and the houses. Since other Monongahela sites do

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exhibit these trenches, it is possible that they also had structures with wattle

and daub construction.

The village organization at the Miley site was typical for Luray Focus

sites - a stockade surrounding a series of pits and numerous postmolds from

house outlines. Five structure outlines were determined and the one concluded

to be typical of the house structures at the site was circular, approximately 23

feet in diameter, with two trash pits inside the structure (MacCord and Rodgers

1966:10). Seventeen pits, eight of which were burials, were excavated at the

Miley site. All of these pits had straight sides and rounded bottoms. Finally,

one stone lined hearth was excavated outside the stockade line. Archaic

artifacts found in conjunction with this feature indicate that the hearth was not

Late Woodland but was associated with an earlier occupation.

The Bowman site, located approximately ten miles north of the Miley site,

was considered by the excavators to be a typical Luray Focus site. The

excavations at this village uncovered twelve pits and twenty postmolds. Three

of these pits contained human remains with the remainder of the pit containing

general trash fill. Three other pits contained only burials and the remaining pits

contained only trash fill. Many of the pits appeared to have been originally

used as storage and were then later filled (MacCord 1964:44-45).

Unfortunately, not enough of this site was excavated to determine either

structure size and distribution or general village organization.

The Luray component at the Quicksburg site appears to have been a

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palisaded village of an approximate 300 feet diameter. One circular house

pattern was defined near the palisade line and the excavators conclude that

structures in the village parallelled the palisade with the central part of the

village open as a plaza (MacCord 1973). Seventeen pits and eight burials were

excavated. Finally, one multiple burial containing 18 individuals was looted

prior to the site excavation in 1969 (MacCord 1973:123). Given that multiple

interments do not occur prior to Luray occupations in the region, this multiple

burial was probably associated with the Luray component at this site.

Ceramic Artifacts

The predominant ceramic type during the Luray Focus was Keyser Cord-

Marked. Griffin (1944) defines this type as shell-tempered with the interior

surface being roughly smoothed and the external surface cord-marked. The

majority of the rims have vertical cord markings although there are some

rimsherds where these cord-markings are oblique (left to right). Decoration is

limited to the lip and adjacent outer rim area and treatment includes lips with

smoothed surfaces, lips with cord-marked surfaces, transverse incised grooves

on smoothed lips, transverse or oblique cord-wrapped stick impressions,

smoothed lips with circular punctates, rims with small lugs, small loop handles,

and rims with rectilinear narrow line incising and punctates. Although handles

could have been functional, the lug handles found on Keyser ceramics are

small and appear to be primarily decorative. The shape of these vessels differs

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somewhat from ones found in earlier contexts and "...were wide-mouthed jars

with slightly constricted lower rims, slightly expanded bodies, and rounded

bases" (Manson, MacCord, and Griffin 1944:404-405).

The ceramic assemblage from the Keyser Farm site consists of three

different types differentiated by temper: limestone-tempered, shell-tempered,

and grit-tempered (Manson, MacCord, and Griffin 1944:402). All of the Keyser

sherds are cord-marked on the entire body of the vessel. Additional surface

treatment included both vertical and oblique from left to right cord marking on

the rims. A variety of decorations occur on the sherds. Based on the presence

of a majority of shell-tempered ceramics, Manson MacCord, and Griffin (1944)

estimate that the Keyser Farm site dates to "sometime between 1550 and

1650" (Manson, MacCord, and Griffin 1944:413).

Since a published description of the ceramics from the Shepard Barrack

site is not available, an examination of these artifacts was conducted in

December of 1992 by E. Moore. There are two basic tempers used in the

ceramics, shell and sand/small quartz grit. A total of 488 sherds were

examined. Of these, 39% (n=190) are shell-tempered and 61% (n=298) are

sand/small quartz grit-tempered. Surface treatment for both types of ceramics

included plain and cord-marked. Decoration observed includes incising,

notching on the rim, and punctating. These sherds of Shepard and Keyser

wares could represent separate occupations at the site as was hypothesized

earlier by Clyde (1959). The ASM excavations in 1958 and 1959 recovered

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over 1000 sherds (Clyde 1959:9), so it is possible that the assemblage at

NMNH is either from separate work performed at the site and is not from the

ASM work or is a sample of the ASM collections.

As with all of the earlier artifact work at the Hughes site, the descriptions

of the ceramics from the 1937-1938 excavations are from intermittent

observations and from a collection purchased by Stearns from the Yinger

brothers. These observations include limited areas of the site, emphasizing

features, especially burials. The purchased collection included over ten

thousand sherds. Four vessels were reconstructed from these sherds. Three

of these were considered typical for Keyser ceramics by Stearns.

Besides Keyser ware, sherds from some other unidentified wares were

recovered from the early excavations at the Hughes site. These include several

sherds of a stone tempered ware with a heavy collar that was decorated with

parallel cord impression, several sherds tempered with a fine sandy grit, sand-

tempered sherds from a small cup shaped vessel, and a few sherds that were

tempered with crushed quartz. McNett (1975) states that this assemblage is

typical for a Keyser site and represents a relatively pure Keyser component.

The 1990/1991 excavations at the Hughes site yielded a ceramic

assemblage very much like that from the earlier work at the site. The figures

presented in this discussion are for ceramics recovered during the 1990

excavations. Similar analysis has not yet been published for the artifacts from

the 1991 excavations. The majority of the sherds recovered in 1990 are shell-

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tempered. Additional tempers include sand, granite, steatite, crushed rock, and

limestone. Surface treatment includes both cord-marked and smoothed.

Decoration consists primarily of notches (both cord-marked and smooth) in the

rims and lug handles (Dent and Jirikowic 1990). This assemblage is consistent

with those described above for both the earlier excavations at the Hughes site

and the Keyser ware assemblage from the Keyser Farm site.

Ceramics at the Moore Village site are primarily shell-tempered, cord-

marked, and globular in form "consistent with published descriptions and

illustrations of Monongahela Cordmarked (and Plain), and with those of its

Potomac Valley/Shenandoah Valley variant, Keyser Cordmarked" (Pousson

1983:101). Decoration is primarily on the rims and includes straight or oblique

cord-marking, horizontal band-marking, and punctating as well as several

designs on the vessel lip made with a cord-wrapped stick (Pousson 1983:101-

109). Less than one percent of the sherds recovered at this site are not Keyser

sherds. These included sand- and grit-tempered sherds and were not assigned

to any specific type (Pousson 1983:113-115).

Ceramics at the Miley site are primarily Keyser Cord-Marked or Keyser

Plain with small amounts of Keyser Fabric-Impressed and Simple-Stamped in

the assemblage. Keyser wares accounted for 98.9% ceramics with minority

wares consisting of sand, gravel, limestone, and siltstone tempered cord­

marked sherds.

Ceramics at the Bowman site are also primarily Keyser Cord-Marked

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with one sherd of the Early Woodland steatite-tempered Marcey Creek Plain

ware in the assemblage. One of the distinctive features of the ceramic

assemblage at the Bowman site is the lack of any other Late Woodland wares,

especially the limestone-tempered Page Cord-Marked that, that are found at

other Luray Focus sites (MacCord 1964:45-47).

The majority of the potsherds at the Quicksburg site are also Keyser

Plain and Cord-Marked. Minority wares include sherds from the sand-tempered

Stony Creek Series, crushed rock-tempered Albemarle Series, and limestone-

tempered Radford Series. It is the Keyser wares that are associated with the

palisaded village occupation at the site.

Lithic Artifacts

There is not a great deal of variety among the formal stone tools from

Luray Focus sites. Projectile points range in size but are primarily triangular.

Ground stone artifacts include celts, hammerstone, pipes, netsinkers, etc. but

do not appear in large quantities when compared to the number of objects from

other artifact classes such as bone, antler, or pottery.

In addition to the triangular forms, points from the Keyser Farm site

include stemmed, unspecialized bifaces, and drill-like points. Points are made

of quartz, quartzite, flint, jasper, rhyolite, chalcedony, shale, and chert,

(Manson, MacCord and Griffin 1944:398-399). Ground stone tools recovered

from the Keyser Farm site are celts, pipes, two fragments of a tablet-shaped

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object, pitted and plain hammerstones, one net sinker, one cupped stone, one

broken discoidal, and three abraded stones probably used for sinew processing.

Finally, several small fragments of limonite with worn edges and a sandstone

palette with ochre stains were recovered.

Stone tools from the ASM excavations at the Shepard Barrack site

(n>400) include two basic classes of tools - large crude bifaces made of

quartzite and small triangular quartz projectile points (Clyde 1959:9). Similar

artifacts were observed by Moore in the collection at NMNH, although not in the

quantities that were reported by Clyde.

Although Stearns (1944) does not discuss the lithic artifacts from the

Hughes site, McNett (1975) provides a brief description resulting from a later

analysis of the entire artifact assemblage purchased by Stearns and now

curated at NMNH. In brief, the projectile points are typically quartz, triangular,

and range in size from small to medium, with medium sized points being the

rarer of the two sizes. In addition to the points, eight celts, an unspecified

number of hammerstones, a piece of rubbed hematite, and two gorgets of

purple slate are in the collection.

The 1990 excavations at the Hughes site yielded a similar formal stone

tool assemblage. Ninety-three complete and 494 fragmentary projectile points

were recovered. These are quartz, quartzite, rhyolite, chert, and siltstone. The

majority of the quartz points are small and triangular. Other lithic artifacts

recovered include bifaces, scrapers, modified flakes, one axe, one celt,

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groundstones, hammerstones, a possible pendant, steatite fragments one of

which may be a portion of a steatite bowl, and fire-cracked rock. Debitage was

categorized into flakes and shatter (Dent and Jirikowic 1990:65-72).

The formal tools from the Moore Village site include ground, rough, and

flaked forms. Ground stone tools include a celt, a large celt fragment, adzes,

three chopping tools, and ten additional ground or pecked tool fragments

(Pousson 1983:91-93). Rough stone tools from the site include eight

hammerstones or hammerstone fragments, anvil stones, grinding stones, and

abrading stones (Pousson 1983:93-96). Flaked tools include small triangular

arrow points, sixteen non-triangular points dating to earlier occupations at the

site, knives, bifaces, blanks, drills, perforators, reamers, scrapers, gravers,

miscellaneous combination tools, pieces esquillees, and choppers (Pousson

1983:57-90). This variety of stone tools provides an extensive stone tool kit,

one fairly typical for Late Woodland villages where a variety of activities were

occurring.

Stone tools in the Miley site assemblage include small triangular

projectile points, drills, scrapers, one celt fragments, one grooved disc, several

hammerstones, one steatite bowl fragment, and one mortar. Forty stemmed

points dating from an earlier occupation were also found at this site (MacCord

and Rodgers 1966:12). The Bowman site yielded a smaller and therefore less

diverse assemblage of small triangular points, scrapers one chipped hoe. No

ground stone tools were recovered at the Bowman site (MacCord 1964:45).

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A variety of projectile points were recovered from the Quicksburg site.

These date from the final Luray Focus component as well as several earlier

components. A total of 218 points were recovered, 198 of which were from the

Woodland. Additional lithic artifacts in the Quicksburg assemblage include

triangulate cores, scrapers, bifaces, utilized flakes, celts, choppers, drills, and

hammerstones. Again, these are all typical stone tools for the Luray Focus.

Worked Bone and Antler Artifacts

In contrast to the lithic artifacts from Luray Focus sites, bone and antler

artifacts are extremely varied. They include functional, decorative, and

ceremonial items and are produced by cutting, flaking, grinding, and polishing

the material. Many of these artifacts, such as "beamers," awls, needles, and

scrapers appear to have been used for hide processing or woodworking.

Others, especially antler tines, were used for stone tool production or were

made into projectile points.

Over 100 bone and antler artifacts were recovered from the Keyser Farm

site. The most unusual of these items were four deer skull and antler

headdresses, three fragmentary and one nearly complete. These were cut

along the skull the antlers were channeled and hollowed posteriorly. It has

been hypothesized that these were worn over the forehead (Manson, MacCord,

and Griffin (1944:394). Only one other such headdress has been found in the

general vicinity, at the Miley site (MacCord and Rodgers 1966). Manson,

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MacCord, and Griffin (1944:394) report that similar archaeological items have

been reported from the Belle Glade mound in Florida and the Hopewell mound.

Additional antler artifacts from the Keyser Farm site include pick-like tools used

for digging, chisels, pottery smoothers, lithic flaking tools, celts, and projectile

points. Most of the antler used was deer, although some was identified as elk

(Manson, MacCord and Griffin 1944:392-398).

Seven pieces of worked bone and antler are present in the NMNH

collection from the Shepard Barrack site. One of these is a bone bead that was

associated with burial #5. Identifiable tools present include two possible

beamer fragments made of deer metatarsals. In addition, there were three

pieces of bone and one piece of antler that were worked but were too

fragmented to identify the type of tool.

Although a complete listing of bone artifacts recovered during the 1937-

1938 excavations at the Hughes site is not available, it is clear that the bone

artifact assemblage is both large and varied and represents a wide range of

activities including hide processing, woodworking, stone tool production,

hunting, and fishing. One of the most prominent types of bone tools at the site

were bone "beamers." These are scraping/defleshing tools made of deer

metacarpals and metatarsals that were used to clean hides. Seventy-nine of

these tools were recovered, including nine complete specimens. The remaining

pieces were all broken in the middle of the bone shaft as the bone grew thin

from use (Stearns 1944:11). According to Roy Brown (1992, personal

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communication), an archaeologist who makes bone tools using primitive

technology, a simple sharp edge on one prominent ridge of the shaft is all that

is needed to construct these tools. After this initial sharpening, the shaft wears

quickly and the tool is exhausted with cleaning as few as two deer hides. The

relatively large number of these tools indicates that hide processing was

probably an important activity at the Hughes site.

The most ubiquitous bone tools recovered at the Hughes site were awls.

Additional bone artifacts at the site included fishhooks, chisels made from

beaver teeth, pendants, and beads. Antler was also used in a variety of forms.

Ten complete and several fragmented antler projectile points were observed by

Stearns, although an unspecified number of additional specimens were

recovered by the Yingers (Stearns 1944:11-13).

Bone artifacts from the 1990/1991 excavations at the Hughes site include

beamers (one complete and several fragmented), awls, and beads. In addition,

several pieces of bone which show signs of polishing and/or use wear but

which are unidentifiable as to specific tool type were recovered. Antler tools

were also recovered and included several scored and broken pieces as well as

antler tines that appear to have been used for flaking tools.

The bone and antler artifacts from the Moore Village site include bird

bone beads and bead fragments, deer bone beads, turtle carapace cup

fragments, awl fragments, bones with smoothed spatulate ends, beamer

fragments, a pendant, one drilled deer phalanx, bone and antler projectile

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points, and antler percussion and pressure flaking tools.

The Miley site contained numerous bone and antler artifacts including

awls, turtle carapace cup fragments, flaking tools, beamers, needles, fishhooks,

points, one tools handle, beads, and one deer antler headdress (MacCord and

Rodgers 1966:12). This last item is the most unusual with the only other

reported headdresses in the region being from the Keyser Farm site.

The Bowman site yielded few bone or antler artifacts. This assemblage

included awls, one needle, one fragmented beamer, one fishhook, two points,

several turtle carapace cup fragments, one tubular bead, and three disk beads

(MacCord 1964:45). The Quicksburg contained a similarly small bone tool

assemblage. The bone and antler artifacts from Quicksburg include seven

turtle carapace cup fragments, one broken bead, one beamer fragment, four

bone awls, one flaking tool, one antler point, and several fragments of scraped

bone and antler.

Mortuary Patterns

Interments within the Luray Focus are varied. They range from individual

to multiple and include flexed, cremation, and bundle burials and were located

in both separate burial pits and in refuse pits. Although some of these burial

positions and treatments had been used at earlier sites in the region, some of

them are new to the Middle Potomac Piedmont area as of this complex. For

example, the Luray Focus has the first frequent use in the region of multiple

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burials.

At least 26 burials were excavated at the Keyser Farm site. Fifty-four

percent (n=14) were adults, seven male and seven female. Of the burials

where position was determinable, nine were loosely flexed, eight were tightly

flexed, and one was extended. The remaining burials had been disturbed or

represented partial skeletons, possibly secondary burials. Orientation of the

intact burials varied and seemed to follow no particular pattern. Eight of the

burials contained grave goods. Six of these were children or infants of

indeterminable sex, one was an adult female, and one was a male subadult.

Five of the children's burials contained beads, typically shell disk beads, copper

disk and tubular beads, and marginella beads. One newborn infant burial was

disturbed but contained two stone projectile points, one antler point, one piece

of worked turkey bone, and one gorget-like piece of felsite. The male subadult

burial had been disturbed by plowing but contained half of an awl or pin that

had been broken by the plow. The adult female burial was the most unusual in

that is showed no signs of disturbance and was fully articulated but contained

none of the larger bones of the lower limbs. Some of the small bones

(phalanges, patella, tarsals, and metatarsals) were present but not articulated.

Associated with this burial was a small jar and a complete turtle shell cup. In

addition, the parietal bones (the side of the skull) were copper stained but no

copper artifacts were recovered. Additional bone tools were in the pit, but it

was not clear whether or not they were directly associated with this individual

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(Manson, MacCord, and Griffin 1944:387-392).

Although notes referring to five burials from the Shepard Barrack site

were observed in the NMNH collections by Moore, no description or discussion

of these has been located. There are ceramics and charcoal associated with

each of these burials in the NMNH collection, but these were mostly small

sherds. It is not known whether these were intentional grave goods or were

recovered from the fill associated with each burial.

As stated earlier, skeletal position was much more varied at sites during

the Luray Focus than at sites from the earlier Montgomery or Mason Island

Complexes. Indeed, the 1937/1938 excavations at the Hughes site alone

revealed all of the above described treatments. Grave goods recovered during

these early excavations consisted primarily of personal adornments in the form

of shell and bone beads and pendants (Stearns 1940:6). Because many of the

burials were looted, no description of all of them exists. It is therefore not

possible to discuss distribution of grave goods or skeletal position in any detail.

The 1990/1991 excavations at the Hughes site revealed burials containing a

total of five individuals. These burials were either exposed or excavated and

reinterred. One of these was an infant burial and contained no identified grave

goods. The second burial contained two disarticulated individuals. One of

these individuals was an adult male and the second was either an adult female

or adolescent male. The third burial also contained two individuals. The first of

these was an articulated adult male in a flexed position with an easterly

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orientation facing north. The second individual was bundled and disarticulated

and was also an adult male. Again, no grave goods were recovered from any

of these burials (Dent and Jirikowic 1990:54).

No burials were reported for the Moore Village site. The Miley site

contained eight burials - two in pits that were also used as trash pits and the

remaining six in pits excavated exclusively for interment (MacCord and Rodgers

1966:12). Three of these burials had been disturbed by plowing and the

position and association with artifacts could therefore not be determined. One

of these three was a multiple burial and the other two contained evidence of

single individuals. The remaining five intact burials were all single and were

flexed or loosely flexed. Four of these burials contained shell and/or bone

beads. One was in a refuse filled pit surrounded by a ring of worn cobbles

(MacCord and Rodgers 1966:12).

Six burials were excavated at the Bowman site. Three of these were in

trash pits and three were in pits used exclusively for interment (MacCord

1964:48). Only one of the burials contained what appeared to be a deliberately

placed artifact. Burial #4, that of a newborn infant, was in a grave pit and

contained a large shell-tempered cord-marked sherd on the skull (MacCord

1964:48).

Eight burials were excavated at the Quicksburg site. Four of these were

in deliberate grave pits and the remaining four were in pits that were

subsequently filled with trash. Two of these contained shell beads - one

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adolescent and one adult male. Two of these were multiple burials - one

containing two children of the same age and the other containing one adult

female and two children (MacCord 1973:128-130).

Subsistence Patterns

Evidence for and descriptions of subsistence patterns at various sites

during the Luray Focus have been described with varying degrees of detail.

These range from the simple observance of cultivars to full analysis and

interpretation of screened and floated sampies of both floral and faunal material.

As with the discussion above of subsistence patterns from the Montgomery

Complex, sites from the Luray Focus containing assemblages that have been

analyzed in detail with the current research (the Keyser Farm site, the Shepard

Barrack site, and the Hughes site) will be described in broad statements in this

chapter and will be described in more detail in subsequent chapters. Luray

Focus sites that have not been analyzed for this research however, will have all

available data presented in this chapter.

Archaeobotanical material from the Keyser Farm site includes abundant

corn, abundant Black walnut (Juglans nigra L.), Big shellbark (Carya laciniosa

Michx. f.), Sweet pignut (Carya glabra Mill.), squash in scarce quantities, and

scarce quantities of papaw (Manson, MacCord, and Griffin 1944:414). Since

both a cultivar and a wild plant were both described as "abundant", this

assemblage suggests that wild plant foods were as important in the diet as

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cultivated plant foods.

No mention of archaeobotanical remains are found in the Shepard

Barrack report (Clyde 1959). One burned hickory nut shell was observed by E.

Moore in the Shepard Barrack collection at NMNH but no corn appears in the

assemblage.

Although it is highly probable that there was corn recovered at the early

excavations at the Hughes site, the report of this work made no mention of any

plant remains, wild or cultivated. The later excavations at the Hughes site

recovered com from an unknown number of pits with a higher concentration of

charcoal and charred corn in at least one hearth feature, Feature 13. Additional

samples of archaeobotanical material were collected during these later

excavations and their analysis will yield additional information about the role of

domesticated crops at this site.

The faunal remains from the Keyser Farm site, the Shepard Barrack site,

and the Hughes site contain a moderate variety of mammals with limited fish,

reptiles, and birds present with deer being the most ubiquitous animal in the

assemblage. Seasonal indicators such as migrating birds, fish, and young deer

are evidence of year-round occupation and hunting at these sites. The taxa

diversity does not represent all of the animals that would have been available at

these sites. Instead, it indicates that there were certain species - deer, turkey,

and turtle - that were being emphasized with other species providing more

minor dietary contributions.

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The analysis and interpretation of the archaeobotanical and faunal

remains from the Moore Village site provides the most complete interpretation

of subsistence patterns for the Luray Focus to date. Material identified by

Gayle J. Fritz from this site consists of one corn cob (Zeamays L.), one corn

kernel (Zea mays), one possible legume, 17 walnut shell fragments ( Juglans

nigra L.), 103 hickory nut shell fragments including Bitternut hickory ( Carya

cordiformis Wang. K. Koch), Shagbark hickory (C. ovata Mill.), Mockernut

hickory (C. tomentosa Nutt.), Sweet (pignut) hickory (C. glabra Mill.), and Sweet

pignut (C. ovalis (Wang.) Sarg.), five hazelnut fragments ( Corylus americana

Walt.), four wild plum pit fragments (Prunus sp.), and one acorn shell fragment

(Quercus sp.) (Fritz 1983:174-175).

Faunal remains were identified by Gregory A. Waselkov and consisted of

25,813 specimens from excavated and screened samples and 1,062 bones

from flotation samples (Waselkov 1983:168). To summarize Waselkov's

findings, three taxa were used as primary meat sources: elk (39%), deer

(33.4%), and black bear (15.6%) (Waselkov 1983:168). This relative

importance of species differs from that seen at the other sites in this study

where deer consistently provides the majority of the meat as reflected in the

archaeological assemblages. Other identified taxa include Cyprinidae,

Semolitus atromaculatus (creek chub), Terrapene Carolina (box turtle), Procyon

lotor (raccoon), and Sciurus niger (fox squirrel). Additional animals mentioned

in this report include frogs, reptiles, wild turkey, ruffed grouse, passenger

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pigeon, gray squirrels, and muskrat. No shellfish was recovered at this site.

Seasonality indicators in this assemblage include the presence of fish,

frogs, reptiles, and migratory waterfowl which could have been obtained in the

spring, summer and fall and evidence of winter-killed deer (Waselkov 1983:168-

170). Two juvenile deer aged four to six months at death were probably winter

kills. Of the two deer frontals in the assemblage, one had antlers intact and

one had them shed. Three adult deer over ten years old were evidenced in the

assemblage by mandibular wear. Waselkov concludes that "Such a pattern of

numerous very young and very old individuals probably indicates that deer were

hunted primarily by individual stalking, an activity associated with egalitarian

tribal societies in the eastern woodlands (Waselkov 1978)" (Waselkov

1983:169). If Waselkov is correct, then differences in the age distribution

patterns between Montgomery Complex and Luray Focus sites could reflect

broad social differences. The implications of Waselkov's thesis will be

discussed in greater detail in the concluding chapter of this work.

Archaeobotanical remains from the Miley site include corn (Zea mays)

cobs and kernels, bean ( Phaseo/us vulgaris?), seed (Pumpkin or squash),

Black walnut (Juglans nigra), and hickory nut (Carya glabra) (MacCord and

Rodgers 1966:13). Animal taxa identified include turkey ( Meleagris gallopavo),

deer ( Odocoileus virginianus), groundhog (Marmota monax), black bear

(Euarctos americanus), beaver ( Castor canadensis), rabbit (Sylvilagus

floridanus), squirrel ( Sciurus carolinensis), box tortoise, and unidentified fish.

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Shell identified includes the Common mussel ( EHiptio complanatus ), the Large

mussel (Lampsilis cariosa Say), and the River snail ( Campeloma decisum)

(MacCord and Rodgers 1966:13). This combination of floral and faunal remains

gives us a general subsistence pattern of crop growing supplemented by the

collecting of wild plants and animals. The diversity of animals at this site is

fairly low with only one bird, one reptile, and a small number of mammals.

Because the fish specimens were not analyzed, the diversity of species cannot

be determined. It is possible therefore, that fish played a more important role

than is apparent at this time. Indeed due to the lack of flotation samples at

many of these sites or the lack of the analysis of existing samples at those with

samples, it is probable that fish are underrepresented at all of them.

The Bowman site yielded few archaeobotanical specimens. These

included one charred hickory nut ( Carya glabra) shell fragment and one charred

bean (unidentified). Identified animals included deer, Common box turtle

(Terrapene Carolina Carolina), turkey, and Passenger pigeon ( Ectopistes

migratorius). Identified shell include Mussel ( EHiptio complanatus) (Most

common), Anodonta cataracta (Say), Lampsilis cariosa (Say), the riverine snail

Campeloma decisum and the land snails Anguispira, Mesodon thyroides (Say),

and Thriodopsis albolabris (Say) (MacCord 1964:48). This data does not allow

much interpretation except that this was a mixed economy utilizing both

cultivated and indigenous species of plants supplemented with hunting and

fishing.

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No archaeobotanical remains were recovered from the Quicksburg site.

Faunal remains recovered included deer, fox, raccoon, beaver, rabbit,

groundhog, turkey, unidentified other birds, box tortoise, mussels {EHiptio), and

one unidentified fish bone. Although no domesticated plants were recovered at

this site, Quicksburg was probably occupied by horticulturalists who

supplemented their diet with indigenous plants, nuts, and fruit as well as a

variety of animals. Because of the lack of further data, more detailed

subsistence patterns cannot be determined at this time.

Discussion

Although the outline above for the progression of cultural complexes may

seem fairly straightforward, in actuality the relationship of these groups both to

each other and to neighboring cultures is still not completely understood. There

are two issues which should be addressed at this point in order to more fully

understand the complexities of the Late Woodland period in the Potomac Valley

Piedmont. The first issue is to what extent were neighboring cultures, such as

Shenk's Ferry and Monongahela, possibly influencing or coming into contact

with the cultures in the study area and what was the impact of that contact?

The second issue is what is the relationship of the archaeological cultures in

the Piedmont to each other? If any (or all) of the three archaeological cultures

discussed above were coming into contact with distinct neighboring cultures

then it is possible that these outside influences could have caused broad

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sociocultural changes which, in turn, affected the hunting strategies of the three

cultures under study.

Some archaeologists contest that the Montgomery Complex may be

related to or influenced by the Shenk's Ferry culture found to the north along

the Susquehanna River in Pennsylvania (McNett, 1993 personal

communication). Shenk's Ferry ceramics are typically tempered with crushed

rock and are often cord-marked and/or incised. Similarities in decoration,

temper, form, and surface treatment lead McNett (1993, personal

communication) to conclude that Shenk's Ferry ware is virtually the same as

Shepard ware and that the assignment of two different types to the same ware

has more to do with categorizing by modern archaeologists than to an actual

meaningful difference in the past. Although temper varies slightly between

these two complexes, this variation in temper could be a result of expediency

rather than a mark of a sociocultural distinction. Ceramics classified as

Shepard ware from the Shepard site included seven different kinds of tempering

material. There are several explanations for this diversity of temper: this could

represent several potters at work at the site; it could represent separate social

units within the population of the site; it could illustrate the incorporation of

techniques from other groups; or, perhaps most likely, this could indicate that

temper was not a meaningful way for the occupants of this site to define and

categorize their ceramics and that temper was used mainly as a functional item

to keep the ceramic from collapsing and not as a symbolic item used for

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identifying a particular group's ceramics. While Shenk's Ferry and Shepard

ceramics are not identical, they do possess many similarities, similarities that

may override their differences and indicate a possible connection between the

groups in the project area with those groups to the north.

The Shenk's Ferry Culture is believed to have had a basic horticultural

economy that was supplemented with hunting and fishing. Larger villages were

located along the river and smaller sites are located in the hills away from main

waterways. One Shenk's Ferry site, the Mohr site, contained a palisade as well

as a circular postmold pattern approximately 30 feet in diameter with an

opening on one side toward a plaza and a possible opening on the opposite

side. The organization at the Murry Site, another Shenk's Ferry site, is similar

to that at Mohr, containing a stockade with a concentric row of house structures

inside and a central structure with no hearth (Kent, Smith, and McCann

1971:334). The presence of a stockade is one major difference between

Shenk's Ferry sites and Montgomery Complex sites. As we have seen above,

Montgomery Complex sites are typically not stockaded.

One similarity in mortuary patterns between the Shenk's Ferry Complex

and the Montgomery Complex is in the type of grave goods. For both cultures,

as with many similar groups, artifacts in adult burials are primarily those used

for personal decoration, such as beads. The most striking similarity in mortuary

patterns between these two complexes, however, is the differential treatment of

infants and children from that of adults. While the treatment itself varies, it is

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the fact that infants and children are sometimes treated differently than adults

that stands out in this examination. In general, it appears that it is infants and

children that most frequently contain deliberate grave goods with adults only

rarely receiving comparable treatment.

There are currently several hypotheses which attempt to explain the

developments and movements of these various groups throughout the region.

One of the more widely accepted of these is that due to increasing pressure

from neighboring groups to the north, the Montgomery Complex people moved

from the Piedmont to the Coastal Plain where they became known

archaeologically as the Potomac Creek Complex (Clark 1980).

The basic premise of this hypothesis is that there were groups of people

from outside the immediate study area, probably from the north or northwest,

shifting their territory and moving into the range of the Montgomery Complex.

In reaction to this external expansion, the people from the Montgomery

Complex then left the Piedmont and the incoming groups eventually become

known archaeologically as the Mason Island Complex (Chase 1988; Clark

1980; Cissna 1986; McNett 1975). There is some evidence that calls this

hypothesis into question. The first evidence is that as has been shown in the

discussion of ceramic traits and mortuary treatment, there are some very basic

similarities between the Shenk's Ferry Culture and both the Montgomery

Complex and the Mason Island Complex. If groups recognized archaeologically

as the Mason Island Complex were expanding from the north (where they are

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known archaeologically as the Shenk's Ferry Culture) to replace groups known

archaeologically as the Montgomery Complex, they would not necessarily have

been hostile groups forcing the local inhabitants to abandon their villages and

move to the Coastal Plain. Rather, these groups could be possible relations

expanding to the south as the result of either population pressure or increasing

hostility from their neighbors. Indeed, if the interaction between Shenk's Ferry

and Montgomery Complex was hostile, then there should be some

archaeological evidence of this at Montgomery Complex sites. While the

position of the Rosenstock site, on a bluff overlooking the river, could be

interpreted as a defensive position, no evidence of a stockade has been located

at this or any other Montgomery Complex sites.

It has been suggested elsewhere (Heisey and Witmer 1964; McNett

1975; Witthoft 1959; Witthoft and Farver 1952) that some Shenk's Ferry people

were forced southward during a hostile expansion of the .

Other Shenk's Ferry peoples stayed in Pennsylvania where there is

considerable evidence for contact between Shenk's Ferry and Susquehannock

peoples. Witthoft (1959) describes this interaction:

As we now understand the historical occupation, the lower Susquehanna Valley in 1570 was occupied by a number of tiny hamlets of Shenk's Ferry people. These folk were of unknown linguistic affiliation and are unknown to history... At certain village sites (including the Shenk's Ferry Site and the Smith Site at Camp Hill, Cumberland County) and at certain river campsites (such as the Brandt Site at Bainbridge and a rock shelter at Casselmans' Run, York County), Susquehannock bands moved into Shenk's Ferry communities, leaving a scattering of pottery and other Susquehannock objects and a few Susquehannock burials... Judging by

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the small amounts of Susquehannock material at these sites, the joint occupation must have been very brief (Witthoft 1959:23-24).

Witthoft goes on to conclude that:

I believe that the Susquehannock material in these Shenk's Ferry sites represents the first stage of Susquehannock occupation of the lower valley and that it also marks the termination of the Shenk's Ferry culture as a separate entity. The Susquehannock bands camped only briefly in these small Shenk's Ferry communities, and then gathered at the Schultz Site at Creswell to establish a large village which included many Shenk's Ferry captives or adoptees (Witthoft 1959:24).

While this late 16th century expansion may indeed be the first Susquehannock

occupation of the Shenk's Ferry area, it is likely that there was previous hostile

contact between the two cultures prior to this expansion and occupation. The

presence of stockades at Shenk's Ferry sites may be defensive measures as a

result of this hostile interaction with the Susquehannock.

The second body of evidence which leads us to question the

replacement hypothesis deals with the relationship between the Montgomery

Complex and the Mason Island Complex. While there are certainly

archaeological differences between these two complexes, there are also many

similarities. Ceramic temper and some aspects of ceramic decoration are

different as are some aspects of mortuary patterns, but general village patterns

remain consistent, as do the lithic and bone tool technologies, certain features

of mortuary patterns, and certain features of ceramic decoration. It is possible

that what has been interpreted as a new culture moving into this area may

actually be change within the groups known as the Montgomery Complex. This

change could be due to increased contact with other groups, rather than a

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wholesale replacement of one group with another. This change could also be

due to change stimulated from within the culture rather than due to outside

contact and influence. It is also possible that if indeed a new group of people

were moving into the Piedmont area, while some members of the Montgomery

Complex people may have moved to the Coastal Plain, some may have

remained in the Piedmont. This idea is supported by the overlap in the ranges

of radiocarbon dates from both complexes. Given the fact that the focus of the

geographic range of Mason Island Complex sites is just slightly upriver from the

geographic focus of sites of the Montgomery Complex, it is also possible that

some people from the Montgomery Complex remained downriver away from the

center of the Mason Island Complex.

The Nolands Ferry site on the Monocacy River contains traits from both

the Montgomery Complex and the Mason Island Complex and can be used to

address this issue of the relationship between the Montgomery Complex and

the Mason Island Complex. The Nolands Ferry site contained Page Cord-

Marked ceramics and Levanna points, artifacts usually associated with the

Mason Island Complex. Four out of five of the burials, however, were flexed, a

position usually associated with the Montgomery Complex. In addition, the

ceramics provide what is not a pure Mason Island Complex combination of

traits. Indeed, Kavanagh notes that:

While Page Cord-Marked ceramics as defined by Griffin are exclusively tempered with limestone, both the Catoctin Creek site and Nolands Ferry have pottery tempered with crushed limestone or quartz, or both, usually collared, and decorated with cord-wrapped stick impressions, punctates

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or incised lines. Some vessels show lugs and castellations. At one range of this ceramic type, these sherds are virtually indistinguishable from the Shepard Cord-Marked (Kavanagh 1982:77).

Peck (1980), in his analysis of the ceramics from the Nolands Ferry site,

found that some of the decoration and surface treatments recovered on the

limestone-tempered ceramics at the Nolands Ferry site are very similar to those

found on other wares. The decoration on some of the sherds from one of the

types defined by Peck, type "C", is identical to Page Cord-Marked sherds found

at the Keyser Farm site. The only difference between them is that the

decoration on the sherds from Keyser Farm is on a collared rim while at

Nolands Ferry, the decoration is on uncollared rims. The decorated collared

rims from Keyser Farm are also found at the Shepard site where they are

classified as Shepard Cord-Marked and tempered with crushed quartz or

granite rather than crushed limestone. This leads Peck to conclude that "The

close similarity in decoration suggests that the type of crushed rock which was

used to temper the vessels was unimportant during this period of the Late

Woodland, and that cultural relationships in this area should be based on the

pattern of decoration rather than on the type of temper which was used" (Peck

1980:10). If this is so, then it would lead us to conclude that the Shepard/Page

and Montgomery Complex/Mason Island Complex divisions may in fact be false

constructions produced by archaeologists and not a reflection of prehistoric

distinctions.

Radiocarbon dates from the Nolands Ferry site fall into four clusters,

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believed to represent separate occupation periods for the site. The four dates

assigned to the Mason Island component at the site are A.D. 1480 (Sl-3880c),

A.D. 1495 (Sl-3882a), A.D. 1550 (Sl-3884a), and A.D. 1590 (SI-3881) (Peck

1980 in Kavanagh 1982:77, 88). Several dates from the Rosenstock site, which

is clearly from the Montgomery Complex, fall within the same range as the sites

from Nolands Ferry leading Kavanagh to conclude that along the Monocacy "at

least for a while the two complexes were overlapping in time" (Kavanagh

1982:77).

In balance, this evidence seems to indicate that at least three of these

Piedmont complexes are related, if not all part of one larger group. This larger

group would include the Shenk's Ferry Culture, the Montgomery Complex, and

the Mason Island Complex with each of these manifestations representing

variants of this larger culture as it changes throughout both space and time.

The degree of contact between these groups may have varied, especially as

unrelated outside groups such as the Susquehannock began intruding. In any

event, given the fairly large geographic range that these archaeological cultures

cover and a time span that covers several hundred years, it is not surprising

that various traits, such as ceramic temper, differ slightly throughout the region

and change over time. These changes do not necessarily indicate the

replacement of one group with another.

As mentioned earlier, some archaeologists believe that the Luray Focus

may be related to, or a southern intrusion of, the Monongahela Woodland

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Complex of southwestern Pennsylvania (Manson et al. 1944; Gardner and

Carbone 1983; MacCord and Rodgers 1966; Schmitt 1952; Pousson 1983; Wall

1981). Monongahela sites center around the junction of the Monongahela and

Youghiogheny rivers but are also found in northwestern Pennsylvania,

southwestern New York, Eastern Ohio, and West Virginia (Kent et al.

1971:336). Monongahela sites are found on either high bottomland areas near

major rivers or on hilltops or saddles overlooking rivers. Although villages vary

in size and structure, most Monongahela villages have a circular ring of

structures with a central plaza area (Wall 1981:30). Houses are mainly oval

(George 1974) although rectangular ones were located at the Montague site

(Butler 1939:12). Hilltop Monongahela villages in Somerset and Fayette

counties are stockaded (George 1974) but stockades are also present in other

areas irrespective of their location on hills or terraces (Griffin 1978).

Monongahela ceramics are primarily shell-tempered with occasional

limestone tempering. Vessel forms are predominantly round-based vessels with

in-sloping shoulders and vertical to slightly flaring or collared rims (Wall

1981:30). Surfaces are plain or cord-marked. Rims are occasionally incised,

lips are plain or notched with some having rises above lugs, and loop handles

occur occasionally (Wall 1981:30).

Monongahela stone tools include triangular projectile points of various

widths and lengths, occasional small-stemmed or corner-notched points, large

triangular or leaf-shaped knives, scrapers, drills, perforators, gravers, adzes,

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celts, hammerstones, and whetstones. Other lithic artifacts include discoidals

and cannel coal pendants (Griffin 1978:558). Bone tools include awls, gouges,

spatulas, fishhooks, chisels, hoes, projectile points, drifts, scrapers, turtle

carapace cups, and beaver incisor chisels. Non-tool bone artifacts include

tubes, whistles, pendants, beads, and perforated canine teeth (Griffin

1978:558). Shell artifacts include hoes, scrapers, and pendants and are found

primarily in western Monongahela sites or near the Ohio Valley (Griffin

1978:558). Griffin (1978:558-559) states that one of the most distinctive

characteristics of is the variety of pipe forms. These

range from visiform stone examples to elbow clay pipes.

Monongahela burials are predominantly single interments although one

pit at the Montague site contained two infants, possibly twins (Butler 1939:13).

Adult Monongahela burials were most commonly flexed while children were

both flexed and extended. Burial goods are predominantly ornamental and

occur with both adult and sub-adult burials (Griffin 1978:557-558).

Subsistence patterns at Monongahela sites consist of a mixed economy

which included hunting, fishing, and growing corn, beans, and squash. The

relative importance of cultivated plants versus indigenous plants and animals is

unclear to date, however Wall (1981:30) states that "subsistence of the

Monongahela peoples depended partially on agricultural products such as corn,

beans, pumpkins, and squash and partially on hunting and gathering." Given

this statement and using the definitions of horticulture and agriculture presented

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earlier, Monongahela cultures could be considered horticultural, not agricultural,

since a marginal dependence on cultivars would not necessarily cause the

rescheduling of time and distribution of labor necessary to be considered

agricultural. Although Wall (1981:30) states that "deer seem to be the best

represented faunal species on Monongahela sites" the relative importance of

various faunal species is generally unknown. In at least one Monongahela site

fish were present in large numbers while deer were not (William Johnson in

Griffin 1978:558).

There are several similarities between the Monongahela and Luray

Focus cultures. In both cultures the majority of sites consist of an array of

structures and pits that are arranged in a circular pattern around a more open

plaza area and are palisaded. Ceramics are shell-tempered, with both plain

and cord-marked varieties. Lithic assemblages from both Monongahela and

Luray Focus sites are very similar with small triangular points dominating the

formal stone tool inventories. Likewise, the bone tool assemblages are also

similar with a variety of tools being produced and the majority of them being

awls or beamers, tools most likely used for hide processing. Some of the dates

from both cultures are relatively close with median dates clustering in the 15th

and 16th centuries. The Moore Village site is thought to have been occupied in

the mid-15th century (Pousson 1983:148) while further down the Potomac, the

Hughes site was probably occupied in the mid-15th century (Dent and Jirikowic

1990:73). Further to the west in the Shenandoah Valley, the Bowman, Miley

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and Quicksburg sites were probably occupied during the second half of the 16th

century (MacCord 1964,1973; MacCord and Rodgers 1966). If the Luray

Focus in the Potomac and Shenandoah valleys is the southern intrusion of the

Monongahela, then it is not surprising that the later dates are associated with

those sites located further away from the original location of the Monongahela.

This hypothesis of a southern expansion of Monongahela replacing the

Montgomery Complex in the Potomac Piedmont and moving further south and

west into the Shenandoah Valley where it is known archaeologically as the

Luray Focus has some obvious implications for the current research. If there

are drastic differences in hunting strategies between the Montgomery Complex

and the Luray Focus as evidenced by the faunal assemblage, then these

differences could be due to cultural or ethnic differences between the two

groups and not simply due to varying dependencies on cultivated plants. The

implications of this hypothesis will be discussed in more detail in the concluding

chapter of this work.

As has been seen above, much is known about certain artifact classes,

such as ceramics and lithics, from the Montgomery Complex and Luray Focus

of the Late Woodland period in the Potomac Piedmont. Other elements of site

interpretation are not so well understood. Village organization and house

structure patterns, for example, are elusive and although hundreds of postmolds

have been excavated at all of the sites discussed above, most of these are in

confusing and overlapping patterns. Differentiating domestic from special

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function structures is also not possible at most of these sites. Because of this

lack of clear data, few definitive statements have been made about social

structure, social differentiation, and social organization at specific sites that are

directly supported by the archaeological evidence. Certainly indirect evidence

can be used but the lack of clear structure forms and the pattern of structures

within a site creates a distinct gap in interpretations of these Late Woodland

sites.

Subsistence systems as well have only been broadly addressed in much

of the work on these sites. The terms horticultural and agricultural are

frequently applied by various researchers to these sites but it is not always

possible to determine what the definitions are for these terms as they are being

used. In some cases, the same sites have been called both terms by different

authors. Montgomery Complex sites, for example, have been referred to as

both horticultural and agricultural depending on the author.

While the current research will not be able to determine exactly what is

meant by all of these terms in previous literature, it will examine these sites

based on the definitions of horticulture and agriculture presented earlier. Since

all of these sites contained corn, it can be stated that food-producing economies

were present throughout the entire time span under examination. The extent of

dependence upon this food production is not clear, however, while it can not be

fully determined at ail of these sites, it can certainly be addressed.

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Conclusion

In conclusion, this chapter has presented a cultural historical context for

the Late Woodland of the Potomac Valley Piedmont region. Key archaeological

features (artifact types and frequencies, village organization, dates of

occupation, possible contact with neighboring cultures, etc.) have been

described for major archaeological cultures during this time period. In addition,

the six sites providing the faunal assemblages for this research have been

discussed in more detail. This context is important in that it provides not only

the background in which to place the broad hunting strategies defined later for

each archaeological culture, but it also provides the specific context for each of

these six sites allowing a more detailed interpretation at the site level. The next

chapter will evaluate the recovery techniques and the resultant faunal

assemblages from each of these sites and will determine which of these

assemblages can be reliably used to define the hunting strategies employed by

the occupants of these sites.

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. CHAPTER 3

ASSEMBLAGE RECOVERY AND UTILITY

Introduction

The purpose of this chapter is to examine the varying excavation and

recovery techniques used at each site. This examination will be used to

discuss the impact that those techniques have had on the utility of the

assemblage for subsistence research. The faunal assemblages analyzed for

this study were collected by various investigators with a wide variety of

techniques that ranged from excavation with no screening and minimal

provenience control to the measuring of three dimensional coordinates and the

recovery of flotation samples. The assemblages were collected by both

amateur and professional archaeologists. All of these variables have played a

role in the completeness, the representativeness, and the research applicability

of the individual assemblages. An evaluation of each of these variables will

allow me to divide the assemblages into two categories - primary and

secondary. Primary assemblages are those with a more representative sample

that can be considered reliable for a subsistence study. Secondary

assemblages are those with samples that are small or non-representative of

86

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subsistence activities but can be used to supplement the patterns found with

the analysis of the primary assemblages. It is the information from the

discussion and analyses in this chapter that will support the determination of

this categorization.

This chapter proceeds with a structured format containing similar

information about the excavation of each site: who performed the excavations,

their research goals or reasons for the excavations, the excavation techniques

used, the presence or absence and degree of screening and/or flotation, the

relative completeness of the curated assemblages (in other words, was

everything that was excavated kept by the excavators or were artifacts

discarded after they were recovered because they were considered unimportant

to the research goals), and where the assemblages are being curated. It is the

biases inherent in all of these factors that will determine to what degree each

assemblage can be used to address the present research questions. The sites

that have been most recently excavated will be examined first and the earlier

excavated sites will follow.

Following this basic information, a brief description of each faunal

assemblage will be given. These descriptions will include results of the

analysis of the faunal remains and will contain information about several

variables including: the number of bones, their size and completeness, taxa

diversity, what portion of the assemblages are worked or show signs of wear,

what portion of the bones are identifiable to class or better, and what can be

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concluded about the degree of impact the field techniques had on the

assemblage. Together, these variables illustrate the relative completeness of

each assemblage and the results of the biases inherent in collection and

research designs.

The majority of these variables will be measured in simple percentages

(i.e., what percentage of an assemblage is identifiable/unidentifiable) (Table 3).

In addition, two indices have been developed, a "bone tool (or utilization) index"

(BTI) and a "measurable (or relative completeness) index" (Ml) (Table 4). The

bone tool index measures what proportion of an assemblage consists of bone

tools. The BTI illustrates if there was a collection bias towards bones

that were worked or utilized. The closer the BTI approaches one, the more

skewed the assemblage is toward containing only those bones that show signs

of alteration. This index includes both those bones that were deliberately

worked and fit into a specific tool class (such as awl, projectile point, beamer,

etc.) and those tools which show signs (such as polish or striations) of having

been utilized without being deliberately altered as a specific tool. An

assemblage therefore with a BTI of one would consist entirely of bone tools and

an assemblage with a BTI of zero would have no bone tools.

The measurable index measures the proportion of bones that are

complete enough and well enough preserved to be measurable. This illustrates

a collection bias towards bones with complete or near-complete diaphyses and

that are readily identified. Given the acidity of the soils in the study area, the

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. TABLE 3

COUNTS AND WEIGHTS OF SPECIMENS BY SITE

Site N % N Gram % Gram Average Weight Weight Weight

Rosenstock 65361 100 107438 100 1.64 Identifiable(Total) 11230 17 61304 57 5.46 ID - Deer 9627 15 50966 47 5.29 ID - Other 1603 2 10338 10 6.45 Unidentifiable(Total) 54131 83 46134 43 .85 UNID - Large Mammal 9890 15 18931 18 1.91 UNID - Other 44241 68 27203 25 .61

Hughes 1 41 100 1317 100 32.12 Identifiable(Total) 31 76 1048 80 33.81 ID - Deer 24 59 633 48 26.38 ID - Other 7 17 415 32 59.29 Unidentifiable 10 24 269 20 26.90 UNID - Large Mammal 5 12 61 4 12.20 UNID - Other 5 12 208 16 41.60

Hughes 2 27178 100 23612 100 .87 Identifiable(Total) 3223 12 9906 42 3.07 ID - Deer 2946 11 9060 38 3.08 ID - Other 277 1 846 4 3.05 Unidentifiable 23955 88 13706 58 .57 UNID - Large Mammal 3557 13 4834 20 1.34 UNID - Other 20398 75 8872 38 .43

Shepard 618 100 2738 100 4.43 Identifiable(Total) 316 51 2111 77 6.68 ID - Deer 99 16 1394 51 14.08 ID - Other 220 36 717 26 3.26 Unidentifiable 302 49 627 23 2.08 UNID - Large Mammal 11 2 93 3 8.45 UNID - Other 291 47 534 20 1.84

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TABLE 3

continued

Site N % N Gram % Gram Average Weight Weight Weight

Shepard Barrack 379 100 1437 100 3.79 Identifiabie(Total) 166 44 1075 75 6.48 ID - Deer 150 40 1014 71 6.76 ID - Other 16 4 61 4 3.81 Unidentifiable 213 56 362 25 1.70 UNID - Large Mammal 154 41 297 21 1.93 UNID - Other 59 15 65 4 1.10

Winslow 1792 100 18621 100 10.39 Identifiable(Total) 1222 68 15633 84 12.79 ID - Deer 671 37 10510 56 15.66 ID - Other 551 31 5123 28 9.30 Unidentifiable 570 32 2988 16 5.24 UNID - Large Mammal 28 2 102 1 3.64 UNID - Other 542 30 2886 15 5.32

Keyser Farm 633 100 4728 100 7.47 Identifiable(Total) 151 24 3585 76 23.74 ID - Deer 138 22 3452 73 25.01 ID - Other 13 2 133 3 10.23 Unidentifiable 482 76 1140 24 2.37 UNID - Large Mammal 30 5 116 2 3.87 UNID - Other 452 71 1024 22 2.27

All Sites Combined 96002 100 159891 100 1.67 Identifiable(Total) 16339 17 94662 59 5.79 ID - Deer 13655 14 77029 48 5.64 ID - Other 2687 3 17633 11 6.56 Unidentifiable 79663 83 65226 41 .82 UNID - Large Mammal 13675 14 24434 15 1.79 UNID - Other 65988 69 40792 26 .62

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TABLE 4

BONE TOOL (BTI) AND MEASURABLE (Ml) INDICES

Site # of # Bone BTI # Meas. Ml BTI+MI Bones Tools Bones 2

Rosenstock 65361 383 .006 1498 .023 .015 Hughes 1 41 38 .93 24 .59 .76 Hughes 2 27178 122 .004 400 .015 .010 Keyser Farm 633 578 .91 66 .10 .51 Shepard 618 390 .63 162 .26 .45 Shepard Barrack 379 7 .018 28 .074 .046 Winslow 1792 341 .19 491 .27 .23 All Sites 96002 1859 .019 2669 .028 .024

degree to which bones were broken in antiquity during butchering and

processing, and the degree of disturbance (i.e., plowing) endured by some of

the sites, it is not likely that a high proportion of bones remain complete enough

to be measured. A measurable index approaching one will indicate whether or

not the more complete and intact bones (as opposed to bone fragments) and

the diaphyses were more frequently collected and curated.

Examining taxa diversity is another way of determining collection biases

(Table 5). Applying taxa diversity to the problem of examining collection bias,

however, has the potential for introducing a basic interpretive assumption. Just

because an assemblage has a relatively few number of taxa does not

necessarily mean that this is a product of excavation and collection strategies.

Rather, it could be that there are fewer taxa in an assemblage because there

were fewer species used by the occupants of the site.

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TABLE 5

NUMBER OF TAXA REPRESENTED AT EACH SITE

Site # of Taxa % Specimens Identifiable to Species

Rosenstock 67 17 Hughes 1 4 76 Hughes 2 26 12 Shepard 13 51 Shepard Barrack 11 44 Winslow 26 68 Keyser Farm 6 24

The problem here, then, is with finding a way of illustrating the degree of

assemblage bias that is due to the collection strategies of the excavators and

not the collection strategies of the hunters. One way to do this is by using the

information given in the various reports and notes of the excavators themselves.

As can be seen below, for many of the excavators, often the reason for

collecting faunal remains was to add to the species list from the site. This

indicates that for these excavations remains should be almost completely

diagnostic with few unidentifiable fragments (such as fragmented long bone

shaft fragments with no diaphyses). Examining the number of taxa present in

an assemblage and comparing it to the size of the site zooarchaeological

assemblage will therefore have to be used in combination with what proportions

of certain sizes of animals are identifiable and which are unidentifiable. For

example, if a site contains 50 mammal bones, all of which are identifiable to the

taxonomic level of species, we can conclude that there was no effort to recover

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all mammal remains, just those which were most diagnostic.

The Rosenstock site (18FR18) provides one the best collections against

which to measure the other assemblages for these variables. Given that one of

the explicitly stated goals of the research at this site was to examine

subsistence patterns, that the researchers at this site performed very detailed

recovery techniques, and the fact that this site was never looted, this

assemblage will act somewhat as a baseline for comparison with other

assemblages where collection bias exists but the effects of that bias are

uncertain.

In short, it is of critical importance to know the excavation and collection

techniques used at each site in order to assess the relative comparability of the

assemblages. Shoveling, troweling, screening, and floating matrix for artifacts

all result in very different types of assemblages. These techniques respectively

increase the detail, degree, and completeness of an artifact assemblage

recovered. It is axiomatic that as more fine-grained recovery techniques are

used, the closer we come to recovering a more complete and representative

sample of the archaeological record. One example that illustrates the impact of

different recovery techniques is at the Apple Creek site in Illinois (Streuver,

1968). Streuver found that by using flotation, over 57,000 artifacts were

recovered that would not have been recovered through standard 1/4 inch mesh

dry-screening. Flotation can have a similar impact on other archaeological

assemblages. The impact that these varying techniques have had on the

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following assemblages will be discussed and illustrated below.

The discussions below about the recovery and evaluation of each site

and its faunal sample are organized alphabetically by site number. An

assessment will be made of each assemblage as a result of these discussions.

In addition, a summary of the results and the assignments of primary or

secondary status for this research will be presented at the end of the chapter.

18FR18 - The Rosenstock Site

Excavation, Recovery, and Curation

The Rosenstock site is an example of modern excavation, recovery, and

curation techniques. Information regarding the excavations at this site

presented in this discussion below are taken from the site field manuals (Curry

and Kavanagh, 1991; 1992) and from personal communications with personnel

at the Maryland Historical Trust, Office of Archeology.

The Rosenstock site was originally discovered in the early twentieth

century but was not extensively excavated until recently. Excavations at the

Rosenstock site began in 1979 and continued during subsequent field seasons

in 1990 and 1991. Research at this site has been co-sponsored by the

Maryland Historical Trust Office of Archaeology, and the Archaeological Society

of Maryland (ASM) as the Annual Field Session in Maryland Archaeology.

Much of the excavation, recording, and laboratory work was performed by

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volunteers organized and trained through the ASM (Curry and Kavanagh

1991:1).

A grid of one meter by one meter squares was established on the site.

Each square was numbered from its southwest corner with a north and east

measurement relative to datum. The plowzone (usually about twenty

centimeters thick) was flat-shoveled by square and all material was screened

through 1/4 inch mesh. Artifacts were sorted by artifact type {i.e., ceramic,

lithic, faunal, etc.) and bagged separately.

Subsoil was encountered directly below the plowzone. The depth below

datum of subsoil was taken at each corner of every square. If no features were

present on the surface of the subsoil, an additional five centimeters was either

flat-shoveled or troweled and screened (Curry and Kavanagh 1991:10-14).

All features were excavated separately from the surrounding general fill

material. Each feature was assigned a unique number and was photographed

prior to excavation. Each feature was bisected twice and excavated in

quadrants. For most of the features, the southwest quadrant was submitted to

flotation and the rest of the feature was screened through 1/4 inch mesh.

Features were excavated in natural levels if they were stratified or in arbitrary

ten centimeter levels if they were not. Feature charcoal was collected when

present (Curry and Kavanagh 1991:15-17).

Postmolds were excavated in a similar fashion. Each postmold received

a unique number, was mapped in place, and photographed. Postmolds were

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bisected, profiled in cross-section and photographed again. The remainder of

the postmold was excavated and all material was screened (Curry and

Kavanagh 1991:17).

The only features that were pedestaled were lithic clusters and hearths.

These were bisected and excavated in arbitrary ten centimeter levels. All

artifacts were left in place as exposed for mapping and photographing.

Charcoal was collected in either plastic vials or aluminum foil and matrix was

submitted to flotation (Curry and Kavanagh 1991:18).

Flotation was performed on site and this material was sorted at the

laboratory. Both light and heavy fractions were recovered. The flotation

material from 1979 has been sorted and samples of it are available for this

study. Although the flotation has been performed for 1990 and 1991, the

samples have not yet been sorted and so were not used here.

Assemblage Description

The complete faunal assemblage from the Rosenstock site consists of

approximately 100,000 specimens. Because of the large amount of material

recovered from this site, not all of it was analyzed to the same degree (see

discussion on levels of analysis in Chapter Four). All feature material

underwent phase two analysis. In this phase, every bone or bone fragment is

analyzed individually. Approximately three-fourths of the plowzone material

underwent analysis. Approximately 10% of the plowzone underwent phase two

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analysis and the remaining 90% underwent phase one analysis. In phase one

analysis each lot of bones was sorted by species or order size (i.e., deer, small

mammal, large bird, etc.) and then counted and weighed by this sort. In

addition, a count of bone tools, altered bones, and butchering scars was noted

for each lot.

As a result of this sampling strategy, over 65,000 bones or bone

fragments were analyzed from the Rosenstock site (see Table 3 for a tabular

display of these data). These specimens weigh a total of 107,438 grams giving

an average weight of 1.64 grams per specimen. Seventeen percent (n=11230)

of this material is identifiable to the level of family or better. The average

weight of the identifiable bones is 5.46 grams and is .85 grams for the

unidentifiable bones. In addition, 18% of the unidentifiable fragments (15% of

the total assemblage) with an average weight of 1.91 grams are from large

mammals. Given the preponderance of deer in this assemblage (see Table 3),

the majority of these large mammal bone fragments are probably deer. The

remainder of the unidentifiable material weighs only an average of .61 grams

per specimen.

These average weights illustrate the effect that the fine-grained recovery

techniques had on the Rosenstock faunal assemblage. This effect becomes

even more notable when the absence of the flotation material is taken into

account. For the 1979 material that was analyzed, there were frequent lots

where there were over 100 bone fragments weighing less than one gram. The

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addition, the flotation material would undoubtedly have reduced the overall bone

fragments average weights even further.

The BTI and Ml are both very low for the Rosenstock site (see Table 4

and Figure 3). Of the 65,361 analyzed bones, only 383 showed signs of

utilization or alteration resulting in a BTI of .006. The Ml for Rosenstock is

.023. The Rosenstock site has the highest diversity of taxa represented at any

of the sites. "Diversity" in these discussions refers to separate taxonomic

classifications at a family level or better. Sixty-seven taxa were recovered from

the Rosenstock site. The next highest number of taxa, 26, was found at both

the Hughes site and the Winslow site. Although part of this difference could be

due to recovery techniques and degree of previous modern disturbance, the

Hughes site was excavated using similar techniques so there must be another

reason for this difference. This reason may well be the prehistoric hunting and

collecting strategies used by the occupants of the site. Further discussion and

interpretations of the implications of this difference can be found in Chapters

Five and Six.

Summary

Due to the undisturbed nature of the site and the excavation and

recovery techniques used, material from Rosenstock comprises the most

complete assemblage in this study. Diagnostic artifacts were excavated and

collected with horizontal and vertical controls and undisturbed feature material

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was submitted to flotation. This effort to recover micro-artifacts adds greatly to

the richness and accuracy of analysis and interpretation. Given the low indices

for this assemblage, and given the proportions of identifiable and unidentifiable

material, it is clear that the excavation and collection strategies had a strong

impact on the completeness of this assemblage. This resulted in an

assemblage that is heavily biased toward a full range of subsistence remains.

18MQ1 - The Hughes Site

Excavation, Recovery, and Curation

The Hughes site was excavated in two major episodes: from 1937 to

1938 and during summer field seasons in 1990 and 1991. Excavation

techniques, collection strategies and research goals were markedly different

between these two periods and therefore resulted in two very different

assemblages. A sample of the artifact assemblage from the 1937-38

excavations are being curated at the National Museum of Natural History,

Smithsonian Institution (NMNH). The artifacts from the 1990-1991 excavations

are stored at The American University (TAU). Both the material at NMNH and

at TAU were examined for this study.

Information used in this discussion is taken from a number of sources.

Primary sources are: a report written by Richard Stearns and published by the

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Natural History Society of Maryland discussing the 1937-38 excavations

(Stearns 1940); a report written by Dent and Jirikowic on file at TAU discussing

the 1990 excavations; personal communications with both Dent and Jirikowic;

and field notes and maps on file at NMNH that were accessioned with the

artifacts donated from the 1937-38 work (Department of Anthropology, SI

accession #186144, #176236, #183968, #191329).

1937-1938 Excavations

The Hughes site was discovered in the spring of 1937 by Nicholas and

Roy Yinger on the property of Mr. Frederick Hughes. The Yingers excavated

approximately two thousand square feet of the site and had uncovered twenty-

six burials and numerous trash pits when the Department of Archaeology of the

Natural History Society of Maryland heard of the excavations. Richard Stearns

and other members of the Society participated in the remaining excavations at

the site until June of 1938. An additional five burials and an unknown number

of pits were uncovered at this time. Stearns and the other Society members

mapped these features and photographed burials uncovered during their

participation (Stearns 1940:1-2).

No grid system is mentioned in any of the discussions of the excavation

nor was any screening performed at the site. The goal of the excavations for

the Yinger brothers was, as Stearns so bluntly put it "...to completely excavate

the site and sell the objects found" (Stearns 1940:1). High market value objects

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do not include large quantities of animal remains that would serve to answer

questions about subsistence patterns. The faunal material that is curated at

NMNH is primarily material that Stearns and others were able to purchase from

the Yinger brothers. From the notes that were made with the accession, this

faunal material appears to be primarily well preserved tools from trash pits and

some burial material. This is confirmed by the discussion of artifact acquisition

by Stearns (Stearns 1940:1-2).

1990-1991 Excavations

This phase of excavation at the Hughes site was funded by the

Department of Anthropology and the Summer Sessions Program of TAU.

Excavations during the 1990 and 1991 field seasons were directed by Dr.

Richard J. Dent, Department of Anthropology, TAU. Ms. Christine Jirikowic

acted as field and laboratory director for the project. Crew for these

excavations consisted primarily of field school students, as well as local

residents who volunteered in the field.

The 1990 and 1991 excavations were performed in three phases: a

walkover visual survey of the project area to identify clusters of surface

material; a series of shovel test pits in an east/west transect across the site to

confirm the results of the walkover survey and to identify intact areas of the site;

and controlled excavation. The site is currently bisected by a series of tree

lines which separate several plowed fields. The orientation of these tree lines

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acted as the grid orientation for the site. The grid north/south axis of the site

was oriented perpendicular to the tree lines. Site datum, a metal pipe set in

concrete, was placed in one of these tree lines (Dent and Jirikowic 1990:41-42).

A metric grid was established over the site and excavation units were

established as two meter squares. Units north of the grid origin point were

numbered (beginning with 1) from west to east in rows south to north. Units

south of the grid origin point were numbered (beginning with 1001) west to east

in rows north to south. It is these squares that provide the horizontal control for

the site (Dent and Jirikowic 1990:44).

Natural stratigraphic levels provided the vertical control for the site.

These levels consisted of a dark brown silty loam plowzone (level one) and a

mottled dark yellowish brown and yellowish red silty clay loam subsoil (level

two) overlying a lighter subsoil. Features occurred throughout the site and,

although they were somewhat disturbed by the plowzone, were generally intact

through Level two. Level one and general fill from Level two was flat shoveled

and screened through quarter inch mesh. Artifacts recovered from this matrix

were bagged separately by square and level. Features were defined with

troweling and were then pedestaled and excavated after the surrounding fill

from each level was removed. Features were cross-sectioned, profiled and

then fully excavated (Dent and Jirikowic 1990:44-48). A sample (one bag) of fill

from each feature was taken for flotation and the remainder of the matrix was

screened through quarter inch mesh (Dent, personal communication). Flotation

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samples were not available for this study. Artifacts recovered from features

were bagged and processed separately from the artifacts from the surrounding

fill.

Assemblage Description

The early excavations at the Hughes site produced an unknown number

of faunal remains. As discussed above, the assemblage at NMNH consists of

only a small sample of the assemblage. In addition, this sample is highly

biased toward bone tools and large identifiable bone fragments. The

assemblage from the early excavations at Hughes consists of 41 bones

weighing 1,317 grams - an average weight of 32.12 grams per bone. This

contrasts sharply with the Rosenstock site where the average bone weight is

1.64 grams and the later excavations at Hughes where the average bone

weight is .87 grams.

Seventy-six percent (n=31) of this assemblage is identifiable and has an

average weight of 33.81 grams per bone. The unidentifiable remains have an

average weight of 26.90 grams. Both of these figures contrast sharply with

those from other sites (Table 3). The BTI and Ml for this assemblage are very

high - .93 and .59 respectively. These indices are higher than those from any

other assemblage (Figure 3). Of the 41 bones in the assemblage, 38 of them

were bone tools and 22 were measurable.

The number of taxa in the assemblage from the early Hughes site

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excavations is low at four (Table 5). Most of the material from this site are

bone tools made of deer bones. Many of these are metapodial bone beamers.

The remaining identifiable material is elk, bear, and turtle.

A total of 27,178 bones or bone fragments were analyzed from the 1990

and 1991 assemblages. These weighed 23,612 grams for an average weight

of .87 grams per specimen. Only 12% (n=3223) of the specimens are

identifiable to the level of family or better. The average weight of the

identifiable bones is 3.07 grams and is .57 grams for the unidentifiable bones.

Fifteen percent of the unidentifiable bones (13% of the entire assemblage) is

large mammal. As with the Rosenstock site, given the preponderance of deer

remains, most of this material is probably deer.

The BTI for the 1990/1991 material from Hughes is .004 and the Ml is

.015. This contrasts sharply with the indices from the early excavations at this

same site. These are the lowest indices for any of the sites in this study (Table

4). Only 122 bones showed signs of deliberate alteration or use wear. Of the

27,178 bones recovered in this sample, only 400 of them were measurable.

These figures correspond with the identifiable/ unidentifiable ratios for

this assemblage. They also differ only slightly from the Rosenstock material.

Rosenstock had 17% identifiable material and Hughes 1990/1991 had only

12%. The Hughes 1990/1991 assemblage consisted of numerous small

fragments of large mammal bones, many of which were difficult although

possible to identify. Rosenstock, in contrast, contained a lot of large bones with

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distinguishing features that were relatively easy to identify and a lot of very

small bones and bone fragments that could not be identified. Rosenstock did

not contain as many of the larger bones broken into small denser pieces as

were in the Hughes 1990/1991 assemblage. This difference may be a result of

how the bones were processed in antiquity. One explanation for this could be

that the occupants of the Hughes site were breaking the bones into small

fragments for degreasing and the occupants of the Rosenstock were not.

Although modern plowing could account for some of this difference, this pattern

carries into the feature material as well, so other explanations must be posited.

As already mentioned, there were 26 taxa in the Hughes 1990/1991

assemblage. These include large mammals, reptiles, amphibians, birds, and

fishes representing a full range in the size of remains recovered. Because

there are a number of specimens representing a variety of small animals, this

relatively low number of animals represented is probably primarily due to

prehistoric hunting patterns and not the excavation and recovery techniques

used.

Summary

Because of the nature of the collection strategy during the 1937-38

excavations, the assemblage housed at NMNH does not appear to be of much

utility for subsistence reconstruction and interpretation. The 1990-1991

assemblage, on the other hand, is applicable to the research questions being

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addressed here. These latter excavations were collected with both horizontal

and stratigraphic control. All matrix was screened and can be used to address

both the diversity and the richness of the faunal assemblage. It is this

assemblage combined with the material from the Rosenstock site that

comprises the majority of the data for this study. The 1937-38 material will be

used as supplemental material for the more recently collected assemblage but

will not be used independently for interpretations.

18MQ3 - The Shepard Site

Excavation, Recovery, and Curation

The Shepard site was excavated in three major episodes. These were

from 1936-1939, 1952-1955 and 1955. These excavations were performed with

a wide range of recovery techniques and provenience control. The artifacts

from the first and last phases of excavation are housed at NMNH. It was this

combined assemblage of faunal remains that was examined for this study

(Department of Anthropology, SI accession #219120). The disposition of the

artifacts from 1952-55 is not known.

The information presented here regarding excavation and collection

techniques is taken primarily from a publication entitled "The Shepard Site

Study" (MacCord, Slattery, and Schmitt 1957). Supplemental artifact

information is from accession notes located at the Department of Anthropology,

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Smithsonian Institution. These notes were constructed when this assemblage

was donated to the museum by Richard Slattery and Hugh Stabler. They

consist of an artifact inventory as well as an inventory of and preliminary

information regarding the burial remains recovered from this site. Except where

noted, all information in the following discussion is from the 1957 site report.

1936-1939 Excavations

The Shepard site was originally located in September of 1936 by Stabler

and Slattery during an archaeological reconnaissance. After gaining permission

for excavations from the owner of the property, John B. Shepard, they

established a site grid and excavated in five-foot squares. Two base lines were

established to form the site grid. A north/south line was marked at five-foot

increments alphabetically from north to south and an east/west line was marked

at five-foot increments numerically from west to east. Each feature was given

an individual number and the provenience of all features refers back to the

letter/number grid coordinate (i.e., A12). These grid coordinates (and,

occasionally, feature numbers) are present on many of the artifacts in the

assemblage at NMNH. Unfortunately, the grid map of these excavations was

lost, so the artifacts analyzed for this study cannot be placed within a horizontal

framework.

Slattery, Stabler, and other volunteers excavated over two thousand

square feet, focussing on the western half of the site. In this area, they

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. excavated nineteen burials and at least fifty pits. Testing in other portions of

the site revealed an unspecified number of pits and nine additional burials.

Dr. William Strong of the Bureau of American Ethnology and Dr. Waldo

Wedel of the U.S. National Museum acted as advisors for the excavation,

mapping, and preservation of artifacts. In addition, Dr. Wedel's field notes were

incorporated into the published report on the site. Additional information on the

1936-1939 excavations was taken from a report written in 1940 by Schmitt and

Slattery.

Excavation consisted of flat shoveling through surface and/or plowzone

material to reveal pits, postmolds, burials, hearths, and other features. Feature

material was then excavated as a unit separate from the surrounding fill. None

of the records of this period indicates screening of any matrix, either fill or

feature material. Material that was considered important to the research goals -

primarily projectile points, potsherds, bone tools, grave goods, and human

remains - was collected and inventoried.

Although no screening was performed, these were systematic

excavations which included horizontal control and curation of a portion of the

assemblage. The primary goals of these excavations were cultural historical.

Research interests focussed on detailing cultural chronology in the area,

collecting information on comparative "culture trait" information, and constructing

broad descriptions of the lifeways of the people who inhabited this site.

Subsistence information collected at this time was equally broad in

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scope. The presence of corn indicated that food cultivation was in use and a

species list was constructed from the faunal remains collected. Since no

screening was done, much of the diversity and richness of the faunal

assemblage may well have been lost in the field. Relative amounts of species

present at the site were not needed to answer the question of what was being

hunted so a simple presence or absence of a particular species was sufficient

to address the subsistence research goals of this time. A sample of the faunal

remains collected is currently curated at NMNH.

1952-1955 Excavations

Excavations conducted at the Shepard site during this period were

undertaken by Nicholas Yinger and Ralph Fout of Frederick, Maryland. These

excavations were primarily in the eastern and central portions of the site and

covered over seven hundred square feet. No maps of this excavation area are

known. This area, in addition to some random shovel test pitting, revealed at

least three burials and thirty pits. The artifacts recovered during this period

were not analyzed for this study.

1955 Excavations

In 1955, Howard MacCord, with the assistance of several volunteers,

tested the Shepard site with both trenching and the excavation of five-foot test

squares. The trench focussed on the western edge of the site and covered four

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hundred and twenty-five square feet. The five-foot test squares were placed at

fifty-foot intervals across the site, with one additional square placed north of the

center of the site. No screening was performed at this site.

The goal of this testing was to answer questions about the size and

depth of the site, the stratigraphy of the site, and the presence of house

outlines which, theoretically, would be revealed by postmold patterns. With

these goals in mind, all test areas were excavated by natural stratigraphic

levels. Features were also excavated as discrete units and material from both

the general fill and the features was stored separately to facilitate research

concerning the stratigraphic sequencing of the artifacts and the integrity of the

site.

As with the earlier work at this site, subsistence reconstruction was not a

stated goal of these excavations so there was no reason to collect all of the

faunal material encountered. It was hypothesized from the earlier excavations

that the people inhabiting this site were agriculturalists and the examination of

the faunal remains was performed primarily to supplement the list of species

known to have been hunted at this time.

Assemblage Description

The faunal assemblage from the Shepard site consists of 618 bones

weighing 2,738 grams. This yields an average weight of 6.68 grams per bone.

The identifiable portion of the assemblage is 51% (n=316) and weighs an

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average of 6.68 grams per bone. Unlike the assemblages from the Hughes

and Rosenstock sites, the greater proportion of identifiable remains are not

deer. Only 31% (99 out of 316) of the identifiable remains are deer. Of the

unidentifiable portion of the assemblage (n=49), only two (4%) are from large

mammals.

The Shepard site assemblage has a large number of bone tools (390)

yielding a BTI of .63. The Ml for this site is .26. Both of these indices are very

high when this site is compared to Hughes and Rosenstock (see Table 4 and

Figure 3). The number of taxa from this site is 13 (Table 5). While this seems

low in comparison to this figure from the Hughes and Rosenstock sites, it

seems high when the sample size is taken into account. The Hughes site has

twice as many different animals in its assemblage, but has a sample size that is

almost 44 times that of the Shepard site. These figures indicate that the

excavators were interested in collecting both bone tools and a variety of the

species represented at the site - both of which were explicitly stated goals in

their published reports.

Summary

As with the early excavations at the Hughes site, information from the

Shepard site indicates that a representative sample of the faunal material was

not collected. Faunal remains were collected if they were from a previously

unidentified species or if there was something unusual about them (such as

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modification for tool use or signs of use wear). This collection strategy is well

illustrated by the following excerpt from the Shepard site report:

Animal bones were abundant, especially those of the Virginia deer. Literally bushels of such refuse were found, washed and sorted. Most could be identified as deer without further study. Those about which there was uncertainty were identified by Dr. Charles O. Handley, Division of Mammals, U.S. National Museum (MacCord, Slattery, and Schmitt 1957:22).

The species list in the report that follows this statement closely matches

the species identified in the present study. It appears that the assemblage

curated at the NMNH is a combination of both the material identified by Dr.

Handley and a sample of the bone tools. Much of the material from the

assemblage curated at NMNH either matches the species listed in the Handley

report or falls into the modified bone category. It is not known whether the 618

bones in the NMNH assemblage is all of the material that was donated to

NMNH or whether only a sample of the donated material was curated.

It is also impossible to determine what percentage of the artifact

assemblage was donated to the NMNH. In addition, none of the artifacts

recovered by Yinger and Fout were donated to the museum (see SI Department

of Anthropology accession record #186144 for list of materials donated by

Stearns and MacCord). The lack of any of these 1952-1955 artifacts further

adds to the sample bias when comparing what is present in the assemblage to

what was present at the site.

All of these factors - research goals, excavation techniques, field

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recovery, collection, and donation/curation decisions for all three stages of the

excavation - affected the currently available collection. Archaeological

assemblages by their very nature are not equally representative of all activities

present at a particular site. In addition, all archaeological collections are,

because of the limitations of both archaeology's methodology and research

orientations, always biased to varying degrees by the very factors discussed

above. The result of these biases on this assemblage is that this assemblage

cannot be used alone for a detailed subsistence study of the type advocated

herein. This is not to say that there are no valuable data to be recovered from

this material, it is just limited in its scope and application here. It can, however,

be used as supplemental data when examining a series of sites.

18M04 - The Shepard Barrack Site

Excavation, Recovery, and Curation

The Shepard Barrack site was discovered and excavated in 1958 by the

Southwest Chapter of the Archaeological Society of Maryland. At the time of

excavation, the site was located in a plowed field and owned by Mr. Hugh

Beshers. Information regarding excavation and collection techniques used at

this site is taken from a report written by Virginia Clyde (Clyde 1959) and

published by the Archaeological Society of Maryland.

Excavations at the Shepard Barrack site proceeded in two phases. The

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first phase consisted of surface observation and artifact collection over the

plowed field. Artifact concentrations were noted and permission was obtained

to excavate an unplowed area along a fence adjacent to the field. A total of

seventeen five foot by five foot test squares were excavated in the fence area

and an additional seven units were excavated in the field. Units were

excavated in arbitrary levels with the first level being ten inches deep

(approximately the depth of the plowzone) and further levels each three inches

deep. In addition to these test units, a trench of unknown size was excavated

closer to the river to a depth of eighteen inches.

There is no screening mentioned in the Clyde (1959) report. There was

only one intact feature uncovered, a post mold. Artifacts continued to twenty-

two inches below the surface but the majority of the material was recovered in

the plowzone.

Assemblage Description

There are 379 specimens in the Shepard Barrack assemblage weighing

1,437 grams, averaging 3.79 grams per specimen. Forty-four percent (n=166)

of the bones were identifiable, with an average weight of 6.48 grams per bone.

Almost all of these identifiable bones were deer (n=150, 90%). In addition, 154

of the 213 (72%) unidentifiable bones were large mammal, probably deer.

Combined, the deer and large mammals fragments constitute 80% of the

assemblage (Table 3). This pattern reflects both the goals and the techniques

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of the excavation. One of the goals was to expose as much of the site as

possible and collect a large sample of the artifacts that would represent the

variety of animals at the site, not just the bone tools or immediately identifiable

bones. As a result, 56% of the bones are unidentifiable. Because no screening

was performed on the site, most of the remains recovered were fairly large

(average weight = 3.79 grams per bone) resulting in a skewing of the

assemblage toward large mammal bone fragments, even the unidentifiable

ones.

The BTI for the Shepard Barrack site is .018 and the Ml is .074. Again,

this indicates an effort to recover subsistence remains as well as bone tools

and a willingness to collect small bone fragments. Eleven taxa were

represented in the assemblage from this site. Although this figure is low when

comparing it to the more complete assemblages (Hughes 1990/1991 and

Rosenstock), it is high when the sample size is taken into account. When

compared to the Hughes site, Hughes has only 2.4 times as many different taxa

but almost 72 times as many specimens, indicating that recovery at the

Shepard Barrack site was somewhat representative.

Summary

There are several problems that limit the usefulness of this assemblage

for subsistence reconstruction. The first of these is that much of the site

appears to have been highly disturbed by plowing. This is critical at this site

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because it appears that there are two components present. Clyde (1959:9)

does note that the later (possibly Keyser) material is concentrated in the middle

of the site. The material from this area would be the material most relevant

here. An examination of the ceramic artifacts from this site at NMNH by E.

Moore revealed that both Shepard and Keyser sherds were present in the

assemblage. The faunal assemblage could therefore be from both or either

component.

The second problem with this assemblage is that, since there appears to

have been no screening performed, the bulk of the faunal material collected will

fall into the category of large or unusual bones or bone tools. In addition, there

is no mention in the records of what proportion of the material recovered was

donated to NMNH. Again, although this assemblage cannot be used alone for

a discussion of subsistence strategies, it can provide supplemental data when

used in conjunction with the data from the primary sites.

18MQ9 - The Winslow Site

Excavation, Recovery, and Curation

The Winslow site was excavated in two periods: from 1940 to 1941 and

from 1959 to 1962. During the first period, excavations were performed

primarily by Richard Slattery and Hugh Stabler. During the second period,

excavations were conducted by the Southwest Chapter of the Archaeological

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Society of Maryland (ASM). The artifacts from the first period of excavations

were donated to NMNH by Slattery and Stabler.

Information used in this discussion is taken from various publications by

Richard Slattery (Slattery 1960a, 1960b, 1961, and 1966/1968). The first three

of these are progress reports concerning the excavations from 1959-1962. The

final reference listed above is what appears to be a draft of a full report and

interpretation of the site, including the data from both excavation periods.

Some sections of this report were written in 1966 and others in 1968, hence the

multiple date for the reference. The entire report is currently on file in the

Anthropology Archives at NMNH.

It should be noted at this time that since the construction of the

Chesapeake and Ohio Canal had destroyed half of the site, the discussions

below refer only to the portion of the site that remained on the north side of the

canal.

1940-1941 Excavations

As mentioned above, from 1940-1941 Richard Slattery and Hugh Stabler

performed excavations at the Winslow site. This work was limited in that the

landowner allowed excavations to be performed with the condition that all areas

had to be refilled at the end of each day. Excavation centered in the west half

of the site and a total of three burials and approximately ten trash pits were

located.

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Horizontal control was of major concern to the excavators and site

datum, referred to as a "base stake", was placed along a fence that bordered

the canal (Slattery 1966:3). Features were measured to this base stake so that

they could be reopened in the future. Given the daily time constraints, the need

to refill every unit, and the size of the site, many features were opened one day,

partially excavated, backfilled, and never completely excavated. No screening

was performed during these excavations. When faced with this situation - a

large village site with numerous pits and burials containing large quantities of

artifacts and excavations that could be stopped by the landowner at any time -

Slattery and Stabler altered their excavation strategy and the goals of the

project. As Slattery states "The objectives of the 1940-1941 excavations then

changed from one of careful documentation to one of obtaining the most

knowledge from the site under restricted working conditions" (Slattery 1968:3).

1959-1962 Excavations

The excavation of the Winslow site from 1959-1962 was performed

largely by members of the ASM with counselling from Slattery. These

excavations were triggered by the fact that a local collector had discovered the

site and had begun excavating and removing artifacts. The landowner at this

time, Mr. Brockett Muir, granted the ASM permission to do unlimited

excavations.

There were two major goals of the ASM excavations. The first of these

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was to confirm whether or not a ring of pits circled the site, an observation that

Slattery and Stabler had made earlier. The second goal was to "obtain any

other additional information available" (Slattery 1968:4). In order to address the

first goal, it would be necessary to correlate the results of the two periods of

excavation. Unfortunately, the 1940-1941 site datum could not be relocated, so

a new site datum was established. This datum consisted of a pipe set into the

ground at the foot of a large elm tree along the bank of the canal. A base line

was established perpendicular to the canal (compass bearing N 31 E) and

extended ninety feet through what was considered the middle of the site. A grid

of five foot squares was then established along this baseline (Slattery 1968:4).

The first area to be excavated was a trench measuring ten feet by forty

feet running parallel to the baseline. Squares were opened adjacent to this

trench and a total of one hundred and ninety four squares were excavated. In

addition, squares were expanded if features were present and extended beyond

the square boundaries. Additional testing elsewhere on the site was done

bringing the total area excavated to approximately five thousand square feet

(Slattery 1968:5).

Standardized excavation techniques were developed for this later phase

of work. As with the Shepard Barrack site, approximately the first ten inches of

soil was plowzone material. This "Zone A" contained prehistoric, eighteenth

century, and modern material (Slattery 1960a:14). All artifacts were collected

and labeled as surface finds and were stored separately from the remaining

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stratigraphically intact material at the site.

Underlying the plowzone was "Zone B", a dark humic soil containing only

prehistoric artifacts. This ranged from eight inches to fourteen inches in

thickness. Zone B terminated at a light yellowish tan colored subsoil. This

interface was considered the existing surface at the time of occupation.

Features extended from zone B into the subsoil and it was zone B that

contained all of the midden material. Zone B was excavated first in six inch

levels, and later in four inch levels to gain more vertical control of artifact

provenience (Slattery 1968:5-6).

Refuse pits were excavated as separate units within each square to

ensure the separation of pit and general fill material. These pits were not

excavated in levels within the pit, but were excavated as a single entity on the

assumption that they were small enough to have been rapidly filled and

therefore probably represented either a single fill episode or relatively few

episodes fairly close in time. Some, but not all, of the pits were bisected and

drawn in profile (Slattery 1968:7-8). These pits seemed to be in a circular

pattern (Slattery 1960b:14). No screening was performed during these

excavations.

The Winslow site contained both human (twelve) and dog (six) burials.

All burials were completely exposed in situ for recording. Burials were given

sequential numbers as uncovered and artifacts from them refer back to this

unique number. Burials were photographed and then excavated (Slattery

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1968:4-9).

One rectangular shaped (possibly storage) pit was excavated. This had

a stone floor and several artifacts but contained little other cultural fill (Tidwell

1960:8-10). In addition, a series of postmolds was excavated which bisects the

arc of pits (Slattery 1960b:15).

Assemblage Description

The assemblage from the Winslow site contains 1,792 bones weighing

18,621 grams for an average bone weight of 10.39 grams (Table 3). The

greater proportion of this assemblage is identifiable (68%) with an average

bone weight of 12.79 grams per bone. Of this identifiable bone, only 37%

(n=671) is deer. Surprisingly, 95% of the unidentifiable remains are not large

mammal. This assemblage does, however, have a high average weight of 5.32

grams per specimen for non-large mammal material.

Of this assemblage, 341 of the bones were bone tools and 491 were

measurable. This results in a BTI of .19 and an Ml of .27. Twenty-six taxa

were recovered from this site. This number is very high - equal with that from

the 1990/1991 excavations at the Hughes site. This is very important, given the

fact that many different animals were recovered without screening or flotation.

Summary

As with the other sites in this study, excavations were performed using a

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combination of flat-shoveling and troweling. There is no mention of screening

for either period of work.

One very useful feature of this assemblage is that almost every bone is

labeled with a site catalog number. The 1966/1968 report contains a copy of

the site catalog appended to the back of the report. Catalog numbers appear to

refer to bulk (as opposed to individual) artifacts that were separated by

provenience. The catalog contains the catalog number, square, depth, and

comments. Because these catalog numbers were noted during analysis, it is

possible to determine whether the remains came from primary contexts (such

as trash pits and burials), from general fill, or from disturbed contexts such as

plowzone or rodent burrows.

One of the more interesting results of this examination is the high

number of taxa observed in the assemblage. Since no screening or flotation

was performed at the site, it is possible that the number of taxa in the complete

archaeological assemblage (as opposed to the collected sample) could have

been as high as that from the Rosenstock site. More detailed statistical

examinations of this diversity will be developed in Chapter Five but clearly the

excavators at this site made an effort to collect a diverse sample of the faunal

remains encountered during excavation.

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44PA1 - The Kevser Farm Site

Excavation, Recovery, and Curation

The Keyser Farm site was originally located and excavated in the late

1930s by Carl Manson and Howard MacCord during a site survey in the

Shenandoah Valley. Although located well west of the other sites, this

assemblage was analyzed because, as discussed in Chapter Two, it is related

to the other sites in the study. Further collection and excavation occurred in

1943 by MacCord after a flood when two burials were exposed. Information for

the following discussion comes primarily from a 1944 report authored by

Manson, MacCord, and James B. Griffin. Additional information is from notes,

photographs, maps, and artifact inventories donated with the artifact collection

(Department of Anthropology, SI accession #160002).

Excavation techniques used at this site are similar to those used by the

authors at other sites as discussed above. A datum was established and a grid

of fifty-foot squares was placed over the site. These squares were subdivided

into five foot squares for excavation. Trenches were excavated at the southern

and eastern ends of the site to clarify site boundaries. When features were

encountered with these trenches five foot squares were measured in place. No

screening was performed at this site.

As with all of the other sites, there was a plowzone overlying the intact

prehistoric material. The plowzone was shoveled and artifacts from this level

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were labeled as surface material. Most of the features were located at the

horizon of the plowzone and the underlying light yellow sandy subsoil. In

squares where features were not encountered, the subsoil was excavated to a

depth of two feet. When features were encountered, the five foot square was

expanded to encompass the entire feature (Manson et al. 1944:377). In several

of the squares there was an artifact rich, dark humic layer between the

plowzone and the subsoil and above any associated features. This was

interpreted as debris that had accumulated in depressions left by settling from

the pits. The bulk of this material occurred in conjunction with trash pits

(Manson et al. 1944:378).

Pits were excavated as a unit and the artifacts from them were bagged

separately from the surrounding fill. Pits were fully exposed and then

triangulated from the square corners. They were then cross-sectioned and the

larger or more elaborate pits were profiled and photographed (Manson et al.

1944:377-378). The majority of the pits appeared to be originally storage pits

that were filled either with trash or by collapse and erosion.

Postmolds were uncovered and excavated over the entire site but there

is no mention of any cross-sectioning of them. Many of the pits appeared to be

in an elliptical pattern and although there were several pits surrounded by

postmolds, there were no clearly definable structures nor were there any

prepared floors uncovered (Manson etal. 1944:386).

Although several of the burials at the Keyser Farm site were located in

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refuse and storage pits, there were also several discrete burial pits uncovered

at the site. All of these were sketched and photographed and these records, as

well as the original artifact inventories from each of the burials, are available in

the accession records mentioned above (Department of Anthropology, SI

accession #160002).

Assemblage Description

The Keyser Farm site faunal assemblage contains 633 bones weighing

4,728 grams for an average weight of 7.47 grams per bone. Identifiable

remains account for 24% (n=151) of the assemblage. Of these, 138 (22%) are

deer. As with the Winslow site, a surprising number (n=30, 94%) of non-large

mammal unidentifiable remains was collected with an average weight of 2.27

grams.

Bone tools account for 578 of the bones in this assemblage yielding a

BTI of .91. Measurable bones total 66 for an Ml of .10. Clearly, this

assemblage is highly skewed toward bone tools. The number of taxa at this

site is very low at six. There are very few small mammals represented in this

assemblage, and most of the assemblage consists of deer, turtle, and turkey. It

is the larger bones from these animals that are most frequently worked into

bone tools.

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Summary

Most of the material at this site was excavated by flat-shoveling and

troweling. No screening was performed. Care was taken during these

excavations to collect as much information as possible about the presence of a

stockade (none was located), the size and shape of structures (both house and

storage), mortuary behavior, and other elements that would eventually appear

as a "culture trait" list (see trait list on pp. 400-401 in Manson et al. 1944).

These lists were developed for most of the sites excavated during this period to

facilitate comparison of sites throughout the Potomac Valley. Indeed, similar

culture trait lists were being developed by many ethnographers and

archaeologists at this time as a tool for comparative research.

Subsistence questions were addressed through both the floral and the

faunal remains at this site. As with the Shepard site (18M03), great quantities

of faunal material are mentioned in the report but are not present in the curated

assemblage. The 633 bones and bone fragments in the assemblage at NMNH

do not constitute the "bushels of animal bones and the pecks of mussel shells,

which indicate the great dependence placed on the animal kingdom as a source

of food" (Manson et al. 1944:414). With this assemblage, it is the bone tools

and the larger pieces that were collected. As with many of the collections, the

use of this assemblage for subsistence reconstruction is highly limited. This

assemblage could not be used independently when discussing subsistence

strategies but can be used to provide supplemental data when comparing it to

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other more complete assemblages.

Conclusion

This chapter has used both a review of documents and a variety of data

to address the issue of the utility of the faunal assemblages for addressing

subsistence questions. The utility of the assemblages varies greatly from site

to site. This range of utility goes from the Rosenstock and Hughes 1990/1991

assemblages, which are well collected and applicable to the present research

questions, to the early excavations at the Hughes site, which are so

dramatically biased towards bone tools that application to the current research

is extremely limited.

The results of this examination are that only two of the assemblages -

Rosenstock and Hughes 1990/1991 - can be considered primary assemblages

as defined in Chapter One. The remaining assemblages, Shepard, Shepard

Barrack, Winslow, and Keyser Farm, are classified as secondary assemblages.

These can be used only as supplemental comparative data and not used to

make initial interpretations about prehistoric subsistence strategies. It is the

primary assemblages that must be used for these statements and

interpretations.

The biases affecting the collection of these assemblages have been

examined through a variety of literature including both published articles and

field notes and then addressed with a variety of indices and descriptive

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measures. All of this information must be taken into account when

interpretations are made based on comparisons between sites.

The following chapter describes the analytical methods used for

collecting the data needed to address the research questions defined in

Chapter One. Given the historical and cultural context described in Chapter

Two and the conclusions regarding the utility of each of the samples in the

current chapter, different sampling strategies were developed for each of the

assemblages. These sampling strategies, as well as the specific analytical

methods used for collecting the zooarchaeological data and the statistical

methods used for later interpretation of the data will be defined in Chapter Four.

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ANALYTICAL METHODS

Introduction

Given the research questions discussed in earlier chapters, the collection

of faunal assemblages analyzed here provides a unique set of data with which

to address issues of animal exploitation in a context that was possibly

becoming increasingly socially and economically complex, whether from

internally stimulated change or as a result of contact with outside cultures. The

sites that are being examined represent a temporal range at a time when there

was a possible increase in the cultivation of plant foods. The idea that these

people were also becoming increasingly committed to a sedentary way of life

can be directly addressed by examining the vertebrate faunal remains.

Addressing these questions using a number of assemblages that were

collected using widely varying excavation and recovery techniques presents

some difficult methodological problems. The varying size and nature of the

faunal assemblages require different sampling procedures and interpretive

assumptions for each site. For example, the assemblage from the Shepard

site, consisting of 618 specimens and excavated fifty-five years ago, was

130

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completely analyzed. The assemblage from the Rosenstock site, however,

where all material was screened and large portions of the site were submitted

to flotation required designing a sampling strategy in order to deal with the

approximately 100,000 bones recovered from four years of excavation.

This chapter will address sampling issues, in addition to describing the

techniques and conditions used for the identification and analysis of the

vertebrate faunal remains. This chapter is divided into three sections. The first

section will describe the techniques used for analysis. The second section will

discuss the sampling strategies used with each assemblage. The third section

will define the various analytical terms used for the analysis as well as the

methods with which the statistical figures associated with each term were

calculated.

Analytical Techniques

This research was conducted over a four year period at both the

Smithsonian Institution and The American University (TAU). Initial identification

was performed using a combination of techniques including the use of

comparative specimens and published identification guides (Olsen 1964, 1968,

1979; Gilbert 1980). The comparative mammalian specimens and a selection

of bird, reptile, and amphibian specimens that were used for identification are

located at the National Museum of Natural History (NMNH) Archaeobiology

Laboratory, Museum Support Center (MSC), Smithsonian Institution. In

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addition, as complete elements of the smaller mammals were identified in the

site assemblages, they were not repacked but were kept accessible in the

laboratory for comparative purposes.

Four of the assemblages - Shepard (18M03), Shepard Barrack (18M04),

Winslow (18M09), and Keyser Farm (44PA1) - are being curated at the MSC.

They were temporarily moved within the MSC to the NMNH Archaeobiology

Laboratory for identification. The assemblage from the Rosenstock site is

currently on loan from the Maryland Historical Trust and was also identified at

the NMNH Archaeobiology Laboratory. The deer remains from the 1990

excavations at the Hughes site were analyzed at the TAU Archaeology

Laboratory using a comparative specimen on loan from the NMNH

Archaeobiology Laboratory. Non-deer remains from 1990 and the entire

screened assemblage from 1991 excavations at the Hughes site were identified

at the NMNH Archaeobiology Laboratory. Fish and bird remains not identified

at the Archaeobiology Laboratory were identified by Justin Lev-Tov,

Zooarchaeology Laboratory Director at the University of Tennessee in Knoxville

using the U.T. comparative collection.

Three phases of analysis were designed for identification. These are

designated phases one through three, with the phase one entailing the least

detailed data recovery and phase three the most detailed. For all phases of

analysis, bones were first sorted into two categories - identifiable and

unidentifiable specimens. These categories were then divided into more

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specific categories of bones. Identifiable bones were those which were

identifiable to the level of family or better. The remainder were then classified

as unidentifiable.

The term "unidentifiable" as used here can be somewhat misleading.

This term does not indicate that no information could be collected from these

specimens. It does, however, indicate that only a certain limited amount of

information could be collected and that the specimen could not be identified to

family, genus, or species. Specimens that were classified "unidentifiable" could

be identified to class and were coded in broad categories combining size and

class(i.e., small mammal, medium bird, etc.). Fragments which were so small

that they could not even be identified to class were classified as "unknown." In

summary, specimens that were determined to be "unidentifiable" were coded

within three degrees of specificity. These were:

1. specimens coded using a combination of size and class(i.e.,

SMAM (small mammal), LBRD (large bird), etc.)

2. specimens coded using only class(i.e., UMAM (unknown

mammal), UBRD (unknown bird), etc.)

3. specimens coded with UNKN (unknown) where no information on

class distinction could be determined.

In addition to the class identification, any information regarding skeletal

element was recorded. With many of the specimens, it was not possible to

identify specific elements but it was possible to determine general body part

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{i.e., long bone, vertebra, etc.). In these cases, codes for broader body parts

were used. As with the taxon identification described above, there were three

degrees of specificity used for coding element. These were:

1. specimens coded using specific element {i.e., HUMR (humerus),

TIBI (tibia), etc.)

2. specimens coded using general body part {i.e., RIB (rib), PELV

(pelvis), LONG (long bone), VERT (general vertebra), etc.) where

specific element could not be determined

3. specimens coded using UNKN (unknown) where body part could

not be determined.

Each specimen in both the identifiable and the unidentifiable categories

were treated as individual cases. Aggregate data was collected only when

there was more than one specific type of bone where both class and element

were the same {i.e., large mammal long bones) from the same provenience.

Because many statistical packages can weight calculations according to a

numeric value, each fragment can be counted when aggregate data is needed.

In phase one analysis, a list of the animals present and an aggregate

count and weight of all specimens was recorded by provenience unit. A sample

of data from this phase would be "site, provenience, deer, elk, squirrel, large

mammal, fish, total count=53, total weight=77 grams." Although this phase

does not yield data necessary to discuss relative proportions of animals in

these lots, it does provide information on bone fragmentation and the

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distribution of animals horizontally at the site.

In phase two analysis, bones were sorted, and then counts and weights

for each category of animals were recorded by provenience unit. At the

Rosenstock site, these units were lot numbers. At the Hughes site, these units

were actual excavation square numbers. A sample of data from this phase

would be "18M01, square 1054, deer - n=15 weight=30; squirrel - n=2

weight=3; large mammal - n=29 weight=55, etc." This phase of analysis yields

data necessary to discuss relative distributions of animals at the site, as well as

data concerning bone fragmentation and proportions of identifiable/unidentifiable

remains.

Phase three analysis is the most detailed phase of analysis and entails

an individual analysis of each bone or bone fragment. A wide variety of

information was recorded for each bone or bone fragment categorized as

identifiable in phase three analysis. This information included taxon, skeletal

element, side (where applicable), degrees of fusion, sex, relative completeness,

breakage pattern for incomplete bones, presence and degree of burning,

presence of human modification, presence of butchering scars, evidence of

pathological conditions, evidence of animal modification, evidence of

weathering, presence and type of decay, and gram weight. The coding system

for both identifiable and unidentifiable remains is presented below in Table 6.

Weights were taken with an Ohaus model C305 electronic balance readable to

0.1 grams with fraction of gram weights rounded to the nearest gram. A data

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TABLE 6

FAUNAL ANALYSIS CODES

dBASE Field Code/Meaning

SITE (c,3): ROS Rosenstock M 03 Shepard M 04 Shepard Barracks WIN Winslow KF Keyser Farm H1 Hughes site 1937/1938 excavations H2 Hughes site 1990/1991 excavations

PROVEN (c,10): (to indicate provenience of bone - since the contents of this field will vary with each site, definitions of the contents of each field are entered as they are determined)

SCREENED (c,1): (used to indicated recovery technique) U unscreened S screened F flotation

SQUARE (c,8): (square number) VARIES TO CORRESPOND WITH EACH SITE

LEVEL (c,8): (level) VARIES TO CORRESPOND WITH EACH SITE

FEATURE (c,3): (feature number) VARIES TO CORRESPOND WITH EACH SITE

LOT (n,7): (lot number) ONLY ON MATERIAL FROM THE ROSENSTOCK MATERIAL

SPEC_NUM (C,10): (specimen or catalog number)

SPECIES (c,4): (taxon) LMAM unidentifiable large mammal MMAM unidentifiable medium mammal SMAM unidentifiable small mammal UMAM unidentifiable mammal XSMM very small mammal BEAR Bear ( Ursus americanus)

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TABLE 6

continued

BEAV Beaver (Castor canadensis) CANF Dog (Canis familiaris) CANS Canidae CARN unidentified carnivore CHIP Chipmunk (Tamias striatus) CRIC mice, voles, etc. ( Cricetidae) CRVD unidentified Cervid (Cervidae) COON Raccoon (Procyon lotor) DEER Deer ( Odocoileus virginianus) ELK Wapiti (Cervus canadensis) FELS Felidae FLOR Cottontail (Sylvilagus floridanus) FOX Fox LCRN large carnivore LEPS Jackrabbit Lepus( sp.) LUTR River otter ( Lutra canadensis) LYNX Bobcat (Lynx rufus) MINK Mink (Mustela vison) MOUS Mouse MTLN Mountain Lion (Felis concolor) MUSK Muskrat (Ondatra zibethicus) MUST Mustelidae OPOS Opossum Didelphis ( marsupialis) PORC Porcupine (Erethizon dorsatum) RDNT unidentified rodent RFOX Red fox ( Vulpes fulva) SCRN small carnivore SKNK Skunk (Mephitis mephitis) SQRC Eastern gray squirrel ( Sciurus carolinensis) SQRL Squirrel SQRN Eastern fox squirrel ( Sciurus niger) UROC Gray fox ( Urocyon cinereoargenteus) WEAS Weasel ( Mustela sp.) WOOD Woodchuck (Marmota monax) LBRD large bird MBRD medium bird SBRD small bird BIRD unidentified bird BOUM Ruffed grouse ( Bonasa umbellus) BUTE Red-tailed hawk (Buteo jamaicensis)

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TABLE 6

continued

COBR American crow ( Corvus brachyrynchos) COVI Common bobwhite ( Colinus virginianus) CYCR Blue jay ( Cyanocitta cristata) DRYO Pileated woodpecker ( Dryocopus pileatus) ECTO Passenger pigeon ( Ectopistes migratorius) GAVI Common loon {Gavia immer) GOOS Goose (Anserinae) MECA Red-bellied woodpecker ( Melenerpes carolinus) MERG Merganser OLOR Whistling swan (O/orcolumbianus) PASS Perching birds (Passeriformes) PICI Woodpeckers ( Picidae ) PINT Pintail QUIS Common Grackle ( Quiscalus quiscula) TURK Turkey ( Meleagris gallopavo) AMPH unidentified amphibian REPT unidentified reptile BOXT Box turtle ( Terrapene Carolina) CHEL Snapping turtle ( Chelydra serpentina) CHRY Painted turtle ( Chrysemys picta) COLU non-poisonous snakes Colubridae) ( ELAP Coral snakes (Elapidae) EMYD Box and pond turtles ( Emydidae) FROG unidentified frog LACE Lizards (Lacertiiia) LSNK large snake LTRT large turtle RABU Frog/toad (Rana/Bufo) RACA Bullfrog (Rana castebiana) STOD Stinkpot (Sternotherus odoratus) TEST Turtles ( Testudinata) TRIO Spiny softshell turtle ( Trionyx spiniferus) TURT Turtle (unidentified turtle) VIPE poisonous snakes Viperidae) ( FISH unidentified fish ANGU American eel ( Anguilla rostrata) CACO White sucker ( Catostomus commersoni) CATO Suckers (Catostomidae) CENT Sunfishes (Centrarchidae) CHUB Creek chub ( Semolitus atromaculatus)

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TABLE 6

continued

CYPR Minnows (Cyprinidae) HYPE Northern hogsucker ( Hypentelium nigricans) ICNE Brown bullhead (Ictalurus nebulosus) ICTA Catfishes (Ictaluridae ) MOAN Silver redhorse ( Moxostoma anisurum) MOER Golden redhorse ( Moxostoma erythrurum) MOMA Shorthead redhorse ( Moxostoma macrolepidotum) MOSA Striped bass (Morone saxatiiis) MOXO Redhorse suckers (Moxostoma sp.) NOCO Common shiner (Notropis cornutus) OSTE Bony fish (Osteichthyes) PERC Perch-like fish (Perciformes) RAY Ray (Aetobates sp.) SALM Trouts and allies (Salmonidae ) SEAT Creek chub ( Semolitus atromaculatus) SHRK Shark STUR Sturgeon ( Acipenser sp.) MMBR medium mammal/bird SMBR small mammal/bird UNKN unknown

ELEMENT (c,4): (skeletal element) UNKN unknown - used for fragments

Forelimb Elements: SCAP scapula HUMR humerus ULNA ulna RADI radius RCRP radial carpal ICRP intermediate carpal UCRP ulnar carpal PISI pisiform 1CRP 1st carpal 2CRP 2nd carpal 3CRP 3rd carpal 4CRP 4th carpal 23CP 2nd & 3rd carpal fused CARP carpal CRPO carpometacarpus

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TABLE 6

continued

1MTC 1st metacarpal 2MTC 2nd metacarpal 3MTC 3rd metacarpal 4MTC 4th metacarpal 5MTC 5th metacarpal 23MC 2nd & 3rd metacarpal fused METC metacarpal ACRP access carpal

Hindlimb Elements: PELV general pelvis HIM ilium ISCH ischium PUBS pubis SACM sacrum COCX coccyx FEMR femur PATL patella TIBI tibia FIBI fibula LATM lateral malleolus ASTR astragalus CALC calcaneum CTRS central tarsal 1TRS 1st tarsal 2TRS 2nd tarsal 3TRS 3rd tarsal 4TRS 4th tarsal C4TR central and 4th tarsal fused 23TR 2nd and 3rd tarsal fused TRSL tarsal TIBT tibiotarsus TRSO tarsometatarsus CRCD coracoid 1MTT 1st metatarsal 2MTT 2nd metatarsal 3MTT 3rd metatarsal 4MTT 4th metatarsal 5MTT 5th metatarsal 23MT 2nd and 3rd metatarsal fused

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TABLE 6

continued

METT metatarsal

General Limb: METP metapodial PHAL phalanx (general) 1PHL 1st phalanx 2PHL 2nd phalanx 3PHL 3rd phalanx LONG long bone shaft fragment SESM sesmoid CRTR carpal/tarsal

Antler Fragments: ANTF antler fragment ANTP antler pedicle ANTS antler shaft ANTB antler beam ANTT antler tip ANTL complete antler, except tips ANTC antler combination

Skull Parts: SKAN skull with antler attached CRNM male cranium fragment CRNF female cranium fragment PETT petrous/temporal TEMP temporal FACE front 1/3 of skull CRAN frontal/parietal/temporal OCCP occipital region SQUA squamosal BSSK base of skull BASO basio occipital JUGL jugal SKLL general skull fragment SKUL complete skull PMAX premaxillae MAXI maxilla without teeth MAXT maxilla with teeth MAND mandible without teeth

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TABLE 6

continued

MNDT mandible with teeth HYID hyoid

Teeth: The coding system for teeth is based on a character field four spaces wide. Each space represents a discrete piece of information, and the overall tooth description consists of the combination of the information in all four spaces.

SPACE 1: (upper/lower) X unknown U upper L lower

SPACE 2: (permanent/deciduous) X unknown P permanent D deciduous

SPACE 3: (tooth) X unknown I incisor C canine P premolar M molar

SPACE 4: (tooth position) X unknown 1-4

TOTH code used for tooth fragments where none of the previous information is retrievable

Axial Skeleton: CLAV clavicle STRN sternum RIB rib ATLS atlas AXIS axis CVRT cervical vertebra

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TABLE 6

continued

TVRT thoracic vertebra LVRT lumbar vertebra UVRT caudal vertebra VERT general vertebra fragments OSPN os penis

Miscellaneous: PLAS plastron CRPC carapace

SIDE (c,4): UNKN unknown CNTR central LEFT left RGHT right N/A not applicable (vertebra, etc.)

PFUSION (c,1): (fusion stage of proximal end of long bones) F fused U unfused G fusing

DFUSION (c,1): (fusion stage of distal end of long bones) F fused U unfused G fusing

MAND_AGE (n,3): (age of mandibles in months)

SEX (c,1): M male F female U unknown

BREAK (c,4): BRKN broken COMP complete

PATT_BREAK (c,4): (used to describe the pattern of bone breakage) SHFT shaft

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TABLE 6

continued

DSFT distal shaft DEND distal end and shaft PSFT proximal shaft PEND proximal end and shaft PEPH proximal epiphysis DEPH distal epiphysis D1/3 distal 1/3 of bone P1/3 proximal 1/3 of bone 1/2C 1/2 complete 3/4C 3/4 complete D1/2 dorsal 1/2 V1/2 ventral 1/2 COMP complete FRAG fragment ANTI antler intact ANTS antler shed FRNT anterior portion of bone (vert & skull) CENT central portion of bone BACK posterior portion of bone CNTR carapace fragment with no edge portion EDGE carapace fragment with edge

PBREAKAGE (c,4): (used to describe various types of breakage done in antiquity on the proximal end) NONE no breakage SPRL spiral fracture TRAN transverse LONG longitudinal GREN green stick WKBK worked break

DBREAKAGE (c,4): (used to describe various types of breakage done in antiquity on the distal end) NONE no breakage SPRL spiral TRAN transverse LONG longitudinal GREN green stick WKBK worked break

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TABLE 6

continued

BURN (c,4): (degree of burning) WHTE burnt white CARB carbonized, burnt black WHCB white and carbonized combination BRNT burnt SBRN slightly burnt PBRN possibly burnt

BURN_PART (c,4): (used in combination with the above BURN variable to indicate the part of bone burned) ALL all of bone burnt 1/2L 1/2 or less of bone burnt in a longitudinal plane 1/2T 1/2 or less of bone burnt in a transverse plane 1/4 1/4 1/2 1/2 3/4 3/4 P1/2 proximal 1/2 D1/2 distal 1/2 PEND proximal end DEND distal end SHFT shaft only DORS dorsal side RNDM random

HUM.MOD (c,1): (used to indicate evidence of human modification) W shows signs of human alteration, either use wear or deliberate alteration

BUTCHERY (c,1): P possible butchery B butchery scar present

PATHOLOGY (c,1):(used to indicate presence of pathological conditions) P pathology present

ANIMAL_MOD (c,4): (used to indicate evidence of non-human animal modification) CRGN a combination of carnivore and rodent gnawing RGNW rodent gnawed CGNW carnivore gnawed

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TABLE 6

continued

WEATHER (c,4): (used to indicate presence of weathering) UNWT unweathered WTHR weathered

DECAY (c,4): (used to indicate other non-human agents of bone weathering) ROOT root damage MIN mineralization

COUNT (n,4): (total number of bones or bone fragments)

WEIGHT (n,4):(weight to nearest gram)

MEASURE (c.t):(whether or not measurements can be taken) M measurable unmeasurable (blank field)

COMMENTS (c,100): (comments)

PHASE (c,1): (indicates phase of analysis)

P1 COUNT (n,4): aggregate count of all specimens from phase one analysis

P1 WEIGHT (n,4): aggregate weight of all specimens from phase one analysis

LOG_SPEC (c,75): list of animals present in lot from phase one analysis

LOG_WRKD (n,2): number of specimens in lot from phase one analysis that show signs of use wear or human modification

LOG_BUTCHR (n,2)number of specimens in lot from phase one analysis that have butchering scars

IDJJNID (c,2): whether specimen is identifiable or unidentifiable to family or better ID identifiable UN unidentifiable

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sheet was designed for recording observations (Figure 4). The data sheets

were designed to match the fields in the database for ease of data entry. In

addition to the above observed information, all catalog numbers and available

provenience information was recorded with each bone or bone fragment, as

well as key information regarding recovery techniques (i.e., whether the material

was from a screened, nonscreened, or flotation sample).

The coding system used herein was designed after the examination of

several database systems. The database system chosen was dBASE III+, with

much of the statistical manipulation that followed performed in dBASE STATS.

A character rather than a numerically based coding system was chosen to ease

use and editing of the database. Because dBASE is flexible in its field design

and can be designed to accept characters as easily as numerics, character

codes that were abbreviations of the entries were selected. For example, the

code for large mammal was abbreviated as LMAM, medium mammal was

MMAM, etc. The dBASE STATS software can translate this character data into

numeric codes for its statistical manipulation, so choosing character codes did

not limit further analysis. Given these software choices, there was no evident

advantage to choosing or designing a numerically based coding system.

Indeed, this software was chosen precisely because of its user-friendly design

and its flexibility in the ability to accept more descriptive character codes.

Initially, a more detailed system for coding fragments of bone that were

identifiable to skeletal element was developed and tested for the first five

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FIGURE 4

POTOMAC VALLEY FAUNAL ANALYSIS CODE SHEET

SITE SPEC_NUM SPECIES ELEMENT SIDE PFUSION DFUSION MAND_AGE SEX BREAK PATT.BRK PBREAKAG DBREAKAG BURN BURN_PRT HUM_MOD BUTCHERY PATHOLGY ANLMOD WEIGHT COMMENT

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hundred cases. This degree of precision proved to be impractical for two very

important reasons - it slowed the pace of analysis to an extreme degree and

was very cumbersome for data manipulation. In this system bone fragments

were described according to their precise orientation {i.e., proximal, distal,

dorsal, ventral, etc.) within the skeletal element (Table 7). Orientation terms

were used as described in von den Dreisch (1976). I subsequently decided to

modify what proved to be a cumbersome excessive degree of precision and

used a set of broader categories that were, nonetheless, still descriptive enough

to calculate the figures (MNI, MNE, etc. - see discussion later in Chapter Four

defining these terms) that I needed for this research. The data that was

collected under the initial more detailed system was translated into the broader

categories of fragment analysis listed in Table 6 under "Breakage Pattern."

Aging and Sexing of Specimens

Aging and sexing of specimens was performed with only two species -

white-tailed deer {Odocoileus virginianus) and raccoon {Procyon lotor).

Although age and sex of individuals can be determined for other taxa, deer and

raccoon were the only taxa with complete enough appropriate elements and in

quantities sufficient for this information to be meaningful for this research.

Deer

Aging of deer specimens was performed primarily with two techniques -

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TABLE 7

FRAGMENT ORIENTATION FOR KNOWN SKELETAL ELEMENT FRAGMENTS

For those fragments for which a particular piece of information can not be determined, an "X" is to be substituted for the codes listed below.

humerus, femur, scapula: proximal/distal P/D cranial/caudal C/U lateral/medial/both L/M/B end/shaft/both E/S/B

radius, ulna, metacarpals: proximal/distal P/D dorsal/volar D/V lateral/medial/both L/M/B end/shaft/both E/S/B

tibia, fibula, metatarsals, astragalus, calcaneum: proximal/distal P/D dorsal/plantar DIP lateral/medial/both L/M/B end/shaft/both E/S/B

vertebra, pelvis: cranial/caudal C/U dorsal/ventral D/V left/right/both L/R/B end/shaft/both E/S/B

ribs: dorsal/ventral DA/ lateral/medial/both L/M/B end/shaft/both EN/SH/BO

phalanx, metapodials: proximal/distal P/D dorsal/ventral DA/ left/right/both L/R/B end/shaft/both E/S/B

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degrees of bone fusion and tooth eruption/wear patterns. By combining these

two techniques, a larger set of data was gathered for the determination of

demographic and seasonality information for deer hunted at these sites.

Severinghaus (1949) provides a system for aging deer mandibles by

examining dentition (Table 8). Using both tooth eruption and degrees and

patterns of wear, a series of age classes was defined. In this system, a total of

six age classes were defined, which were further subdivided into twenty-three

sub-classes. Dentition pattern is the basis for the definition of each of the six

age classes with degrees of eruption and patterns of wear defining the sub­

classes. Thus, for younger individuals, the pattern of presence or absence of

certain teeth places any particular mandible in a specific age class. Subjective

observation of the wear patterns further places that mandible into a sub-class.

With this technique, certainty in assigning any given mandible to a class

is higher than assigning that same mandible to a sub-class. This degree of

certainty varies for a number of reasons. First, the experience of the analyst

affects the identification of the wear patterns. Second, wear patterns vary

between populations of deer. A particular wear pattern that may be indicative

of one sub-class of aging in one deer population may vary from that of a

different population.

Several efforts were made to alleviate these problems. The first of these

is that all mandible observations were performed at one time. This was done

for two reasons. The first was that by performing all observations at one time,

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TABLE 8

CRITERIA FOR AGE CLASSES FOR DEER (ODOCOILEUS VIRGINIANUS) FROM SEVERINGHAUS 1949

l=incisor; PM= premolars; M=molars

Age Age Range Criteria Class

1 Birth to One Week All I erupted; PM through bone

2 One Week to Four Weeks I show further growth then fully erupted; 1st and 2nd PMs through gum

3 Four Weeks to Ten By the end of the age class, PMs 3/4 Weeks developed; 1st M erupting; slight wear on 2nd PM and anterior cusp of 3rd PM; no wear on 1st PM or on middle and posterior points of the 3rd PM

4 Ten Weeks to Seven By the end of the age class, adult Months pincers fully erupted; wear slight on 1st decid. PM and conspicuous on 2nd and 3rd; slight wear on 1st M; hole formed in jaw for eruption of 2nd M

5 Seven Months to Thirteen replacement of all milk I with permanent Months teeth; 2nd M fully erupted; permanent PM fully formed and can be seen through a small orifice between the roots of the deciduous PMs

Thirteen Months to Twenty Continuation of resorption of jaw around 6 Four Months and Older temporary PMs; from 17 to 20 months permanent PMs erupt; 3rd M fully erupted in the 20 to 24 month range; wear patterns continue for additional sub-classes of this class

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variations in consistency during identification would reasonably be minimized.

The second reason was that by examining all mandibles at one time the entire

sample of mandibles could be observed, thereby aiding in identifying any

general trends that might be present within the entire sample.

The second technique used to minimize observation error was that all

aging of mandibles was done three times over a 12 month period. By

performing the identifications several times and subsequently comparing the

results of all of the identifications, errors due to a misidentification during one of

the observation cycles were minimized. With each observation cycle, the

identification of ages was performed in several steps. In the first step, the

mandibles were sorted in a continuum from youngest to oldest based on tooth

eruption and relative tooth wear. Divisions of age classes based on the

Severinghaus criteria were then determined and the mandibles were assigned

an age class or sub-class when possible. Each mandible was numbered and

the age class was recorded. For each mandible, a "certain" or "uncertain"

determination was made of the age class assignment. In general, if a complete

tooth row was present and the wear pattern was clear, the assignment was

considered relatively certain. If only a partial tooth row was present, or if the

wear pattern did not follow the general patterns observed in the rest of the

mandibles, the assignment was considered relatively uncertain. After each

observation series, mandibles were taken out of age order and stored until the

next observation. Finally, all observations were compared and any

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discrepancies were reconciled.

In addition, measurements of all mandibular teeth were taken.

Measurements were taken from the highest point on the lingual crest to the

lowest point of heavy pigmentation along the gum line. On the three premolars,

one measurement was taken on each tooth. On the first and second molars

two measurements were taken, one on each lingual crest. These two

measurements were averaged for each tooth. Four measurements were taken

on the third molar, one on each anterior crest and one on the posterior cusp of

the third molar. All measurements were taken with a Fowler Ultra-Cal II digital

caliper.

Another procedure for determining ages of deer was developed by

Gilbert (1966) using the examination of annular growth in the cementum of

teeth. This aging method was not used in this research primarily because of

the cost entailed in the preparation of specimens for this procedure. Preparing

thin sections requires specialized training and equipment, neither of which was

immediately available for this research, and the cost of contracting for a series

of sections and slides was felt to be prohibitive. In addition, as discussed

above, although they are not without their faults, tooth-wear estimates are a

widely accepted technique for aging as long as they are substantiated by

independent data and are not used as the sole evidence in a research project.

Observations used in the sexing of deer remains in the assemblages

were much more difficult to make than the observations for aging. One reason

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for this is that the techniques that have been developed for sexing skeletal

remains have a number of drawbacks for archaeological assemblages given

differential representation and preservation of the elements. The two elements

routinely used for sexing deer specimens are pelvis and antlers. Smith (1975)

found that the pelvic sample from a series of Mississippian sites was small due

to the high degree of destruction during butchering. Because of this, a great

deal of the pelvic sample tends to be small fragments not usable for the

morphological examination required for sexing. In addition, doe skull fragments

{i.e., those without antlers) may be under-represented at a site because skull

fragments from bucks are more likely to be brought back to a site where the

antlers were then used.

Antlers on deer, Odocoileus virginianus, occur primarily on males.

Although there are incidences of female deer having antler, the occurrence of

this is not extremely frequent. Goss (1983) states that of modern populations

examined in Michigan, one out of every 900 does had antlers. In modern deer

populations in Pennsylvania, only one out of every 4400 does had antlers.

When present, antlers on females tended to be unbranched spikes unlike

antlers on bucks which can have several beams and numerous tips (Goss

1983). Given the low ratios of does with antlers from modern populations, it is

not likely that does with antlers would have been a significant part of a sample

of individuals from a prehistoric population.

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Raccoon

Aging raccoon specimens was accomplished using a tooth eruption and

wear system. Grau, et al. (1970) present a series of techniques for aging

raccoon specimens including degree of cranial suture closure, dental annuli,

and tooth wear. Because crania of the small mammals in the assemblages

were highly fragmented, degree of cranial suture was not possible for this

research. As with the deer, examining cementum annuli was too costly to be

performed for this research. In addition, Grau et al. (1970) found in their

examination of annuli that the rings were too variable and too difficult to

distinguish to be useful for interpretation. A number of reasons were postulated

for this difficulty, including cementum layers not forming annually and an

inability to differentiate closer layers in older specimens (Grau, et al. 1970:370).

Because mandibles were frequently complete enough for tooth wear

examination it was decided that only mandibular dentition patterns of eruption

and wear would be used for the aging of raccoons in this research.

The techniques used for aging raccoon mandibles are based on the

same premise as with the techniques used for deer - that dentition erupts and

wears in similar patterns as an individual ages. Grau et al. (1970) divided the

various stages of eruption and wear into five classes (Table 9). These are not

divided into further sub-classes.

A system for analyzing the ages of raccoons was designed to minimize

misidentifications. As with the deer, all observations were made three separate

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TABLE 9

AGE CLASSES FOR RACCOON (PROCYON LOTOR) BASED ON TOOTH WEAR FROM GRAU ET AL 1970

Age Age Range Criteria Class

I 0-14 Months Little or no wear on any of the teeth

15-38 Months Wear on buccal side of 1st M and mesial-buccal side of 2nd M but cones still present

39-57 Months Cone on distal-buccal surface of 1st M and cones on buccal side of 2nd M are worn flat; Wear beginning on PMs

IV 58-86 Months 2nd M worn flat; 1st worn flat w/two spots of enamel left; distal-buccal cone of 4th PM absent

V >86 Months 1st and 2nd M flat; distal-buccal cone on 4th PM absent

times over a 12 month period. All mandibles from all sites were aged at the

same time. They were sorted into the age classes defined by Grau et al.

(1970), each mandible was numbered, and data for each was recorded.

Mandibles were then taken out of order and stored until the next observation.

Grau et al. (1970), in their work on aging raccoon mandibles, also

presented a technique for sexing specimens by examining the size of the

canine. There is considerable sexual dimorphism in the root thickness of the

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lower canines of individuals between five months and four years of age. By five

months of age, the lower canine has acquired its maximum root thickness. In

the sample that they examined, all male canines were thicker than four mm and

93% of the female canines were thinner than four mm (Grau et al. 1970:368).

Measurement of size was taken on all available canines from all sites in the

current research. Canines were removed from the mandibles, measured, and

then placed back into the mandible. All measurements were taken with a

Fowler Ultra-Cal II digital caliper.

Butchering Scars

The recording of all butchering scars was performed after the completion

of all other basic analyses. As material was sorted and identified in the phase

one through three analyses, specimens from primary assemblages with

butchering scars were labeled and removed from the rest of the assemblage.

These scars include cut marks, spiral fractures, and heavy blows. Butchering

scars on these specimens were then examined using natural, florescent and

halogen light. Small scars that were visible in natural light were often not

visible in florescent light. In addition, halogen light occasionally allowed the

observation of small scars or cut marks that were not observed using natural

light. No magnification was used to identify scars not immediately visible.

Butchering scars observed on specimens from secondary assemblages were

noted during initial analysis but were not examined in further detail. Because of

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sampling biases discussed earlier, it was decided not to perform any more

detailed analysis on the butchering scars from these assemblages.

A coding system for recording and classifying butchering scars was

developed using Binford's 1981 "Inventory of Described Skinning and

Butchering Marks" (Binford 1981:136-142) as a basic code list (Table 10). This

inventory describes over 100 scars by their location on individual elements. It

also identifies the type of activity associated with each scar. These activities

include dismembering, food preparation, skinning, killing, consumption, filleting,

defleshing, and secondary butchering. Scars which were identified on the

Potomac Valley assemblages and were not included in the Binford inventory

were given a code and were also classified as to probable activity.

Sampling Strategies

The strategies for sampling the assemblages varied according to the

recovery techniques used during excavation. As stated earlier in Chapters One

and Three, the assemblages were divided into two different categories, primary

and secondary, which were defined by the relative completeness of the

recovery techniques used at each site. Decisions were then made as to what

proportion of each assemblage would be analyzed using each phase of

analysis.

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TABLE 10

CODES FOR BUTCHERING SCARS

Code Definition

EM-1 Transverse cut marks across the proximal dorsal surface of the atlas. (The opposite side of Binford's (1981) CV-1)

EM-2 Longitudinal cut marks on the articular processes of lumbar vertebra, (see Binford's (1981) TV-5)

EM-3 Transverse cuts along the inferior surface of the centrum, (see Binford’s (1981) TV-3)

EM-4 Transverse cuts across the posterior shaft of the femur.

EM-5 Longitudinal cuts long the base and lower part of the dorsal spine, (see Binford (1981) TV-2)

EM-6 Astragalus split longitudinally.

EM-7 Dorsal transverse cuts on the atlas.

EM-8 Transverse cuts on rib shaft.

EM-9 Longitudinal cuts on the posterior shaft of the metatarsal.

EM-10 Transverse cuts on the posterior side of the central and fourth tarsal.

EM-11 Transverse cuts on the proximal dorsal surface of the lumbar vertebra.

EM-12 Oblique cuts on the lateral face of the calcaneus.

EM-13 Transverse cuts on the lateral medial side of the first phalange.

EM-14 Transverse cuts across the articular tubercle of the temporal bone where the mandible articulates.

EM-15 Transverse cuts across the shaft of the tibia.

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EM-16 Longitudinal cuts on the triceps brachia of the scapula.

EM-17 Transverse cuts across long bone shaft fragments.

EM-18 Transverse cuts across pelvis fragments.

EM-19 Spiral fracture on long bone shafts.

EM-20 Transverse cuts across the condyles of the tibiotarsus.

EM-21 Cut marks on skull fragments.

EM-22 Transverse cuts across distal shaft on beaver tibia at curve on distal end.

EM-23 Transverse cuts across coracoid shaft.

EM-24 Transverse cuts across the blade of the scapula.

EM-25 Transverse cuts on the posterior shaft on the radius.

EM-26 Transverse cuts across the posterior shaft of the tibia.

EM-27 Transverse cuts across the distal articular shaft of the first phalange.

For all non-EM codes see Binford 1981:136-142.

Primary Material

Primary assemblages were from recently excavated sites where all

matrix was screened. There were two sites which fell into this category,

Hughes (18M01) (1990 and 1991 excavations) and Rosenstock (18FR18).

These two assemblages were fairly large - over 27,000 specimens from

the Hughes site and an estimated 100,000 specimens from the Rosenstock

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site. Given the size of these assemblages, I decided to analyze the entire

assemblages, but to use different levels of analysis for various contexts at each

site. All feature material from the Hughes site was analyzed in full detail using

a phase three analysis (see Chapter Four for definitions of all phases of

analysis). All material from non-feature site fill and the plowzone from the

Hughes site was given a phase two examination. This examination had four

goals: to record aggregate counts and weights for the taxa in the assemblage;

to record any anomalous or unique specimens; to record any specimens that

might be useful for seasonality estimates {i.e., deer mandibles, migratory birds,

etc.); and to record any specimens that showed signs of alteration, utilization, or

butchery for further analysis.

The material from the Rosenstock site provided more difficult sampling

decisions. On one hand, it is a large and very well collected sample, the

majority of which was from undisturbed features - an ideal sample for this

study. On the other hand, this assemblage is so large that because of time

constraints it was not possible to analyze every specimen for this study.

All feature material and all non-feature but non-plowzone (general site

fill) material from the Rosenstock 1979, 1990, 1991, and 1992 excavations

underwent the most detailed phase three analysis. Phase two analysis was

performed on all plowzone material from 1990 and 1991, a sample of 1979

plowzone material, and a sample (28 out of 100 lots) of plowzone material from

1992. Phase one analysis was performed only on the sample of 1979

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plowzone material from the Rosenstock site that was not examined with phase

two analysis (see Table 11). The phase one sample consisted of a portion of

the plowzone material only from non-feature areas. Again, the phase one

examination provides a quick means of getting a list of taxa in the sample, of

identifying any unusual specimens, and of identifying any bone tools without

spending a large quantity of time performing the more detailed analyses.

After examining the preliminary results of the phase one and two

analysis performed on the complete plowzone material from 1979, 1990, and

1991 and the 28 lot sample of 1992 plowzone material, it was determined that

the remaining 72 lots of plowzone material from 1992 would not be examined at

all. The diversity and relative quantities of taxa in the plowzone material was

similar to that found in the features and because of the disturbance and

possibility of contamination in this level, I decided to focus the analysis on the

in situ material. In summary, all in situ material was analyzed to the most

detailed phase three analysis and approximately 80% of the plowzone material

was examined in either phase one or two analysis.

Secondary Material

Secondary assemblages were from sites that had been excavated prior

to the development of modern recovery techniques, such as screening and

flotation. Sites in this category were Shepard (18M03), Shepard Barracks

(18M04), Winslow (18M09), Keyser Farm (44PA1), and early (1937-1938)

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TABLE 11

PERCENTAGES OF ASSEMBLAGES FROM THE ROSENSTOCK AND HUGHES SITES SUBMITTED TO EACH PHASE OF ANALYSIS

Site Phase 1 Phase 2 Phase

Hughes Feature 0 0 100 Non-feature material 0 100 0 Rosenstock Feature 0 0 100 Non-feature material 40 40 0 (estimated figures)

excavations from the Hughes (18M01) site.

The faunal assemblages in this category were relatively small and

consisted mainly of large, identifiable bones or bone fragments, many of which

were worked or utilized. Due to the high degree of bias already affecting the

completeness of these assemblages, 100% of all material from these sites was

fully analyzed.

Definitions of Analytical Terms

The distribution of animal species and of body parts for key species

provides much of the data used to answer the current research questions.

Several ways of quantifying and illustrating these distributions will be used

when comparing assemblages from various sites. Much of this will be done

with frequency diagrams. Several ways of testing subjective observations will

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be performed. Although many of the calculations and terms used here are

commonly used in zooarchaeological analyses it is important to define not only

how they are being used in this study but also exactly how they are calculated.

As discussed by Lyman (1992), quantitative terms may have vague definitions

or several different definitions and can be calculated in a variety of different

ways. Defining the meanings of and the methods for employing these terms

will allow for a clearer understanding of the data presented.

NISP

NISP is the Number of Identified Specimens for a given taxon. A

specimen can refer to either a complete bone or tooth (an element) or a bone

or tooth fragment. Each piece of bone or tooth, regardless of the relative

completeness of the element, was treated as an individual specimen during

analysis. There are three taxonomic levels at which NISP is used in this study:

species, family, and class. The level being used will be specified in all

discussions. For this study, NISP also means that specimens at the level of

family or better were also identified to skeletal element. A specimen was not

assigned to a taxon better than class (i.e., more specific than mammal, bird,

fish, etc.) if it could not be identified to skeletal element. Specimens that could

be identified only to general body part (i.e., long bone shaft or unspecified

vertebra fragment) were assigned to class when possible for taxonomic

identification. The actual NISP calculation was performed by counting the

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number of specimens that fit the category under question (Table 12). In

addition, the relative frequency, or percent of NISP for each taxon, was

calculated and can be found in Table 13.

As with any unit of quantification, there are pros and cons in the use of

NISP. Some of the problems encountered when interpreting NISP are due to

the variability of the impact of taphonomic forces upon different bones both

between elements and between species, as well as the fact that different

animals have different numbers of elements in their skeletons. For example,

some bird bones which are fragile break easier and into more and smaller

fragments than would a mammal bone of a comparable element. Since NISP

measures the number of specimens (which can be fragments) rather than the

number of elements that the fragments may represent, NISP can become

inflated for fragile bones. These taphonomic considerations must therefore be

taken into account when interpreting NISPs.

MNI

MNI represents the Minimum Number of Individuals that would account

for a defined sample of specimens. For this research, MNI was calculated at

the species level for each species represented in each site assemblage. MNI

was also calculated for families or orders when species was not determinable.

For example, MNI was calculated for the family Centrarchidae (Sunfishes) even

though the specimens were not identifiable to species. Calculating the MNI

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Barrack 1 15 1 3 2 - -

______7 7 343 340 993 990 99 99 12 12 TABLE 12 19 75 980 38 26 NISP BY SITE Shepard Winslow Hughes Keyser Farm Shepard - 1 1 1 1 3 5 2 7 4 4 4 13 75 70 32 41 146 3424 3282 3560 Rosenstock Frogs/Toads Eastern Spiny Softshell Box Box and Pond Turtles Lizards Bullfrog ReDtiles Eastern Painted Turtle Eastern Box Turtle Coral Snakes Non-poisonous Snakes Poisonous Snakes Snake Birds Geese Mergansers Snapping Turtle Common Musk Turtle Common Loon Turtle Amphibians Whistling Whistling Swan

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. CT> 00 Barrack 1 1 - - - 1 2 Continued TABLE TABLE 12 13 13 29 41 10 6 Shepard Winslow Hughes Keyser Farm Shepard . - - 1 1 1 1 1 2 3 5 2 8 2 4 2 12 35 115 394 1764 Rosenstock

Birds, Birds, continued Red-Tailed Hawk Ruffed Ruffed Grouse River Chub Pileated Woodpecker Red-Bellied Woodpecker Blue Jay Fishes Passenger Pigeon Pintail Common Bobwhite Big Big Mouth Chub Common Grackle Perching Birds Creek Chub Wild Wild Turkey Woodpeckers Common Shiner Suckers Owl American Crow American Eel

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. CO 05 1 1 335 Barrack 198 1 3 53 19570 Hughes Keyser Farm Shepard 1 5 8 1291

Continued TABLE 12 105 319 Shepard Winslow - 1 1 1 1 1 1 6 2 4 6 4 4 2 4 3 26 24 23 56 Rosenstock

Fishes, Fishes, continued Redhorse Suckers Northern Hog Sucker Brown Brown Bullhead Shorthead Redhorse Golden Redhorse Minnows Perch-like Fish Silver Redhorse White Sucker Catfishes Striped Striped Bass Sunfishes Sturgeon Bony Bony Fishes MammalsEastern Cottontail 40932 Trouts Trouts and Allies Snowshoe Hare (Jackrabbit) Eastern Chipmunk Eastern Gray Squirrel Woodchuck j t Q. C o CD Q. with permission of the copyright owner. Further reproduction prohibited without permission. Barrack Hughes Keyser Farm Shepard

Continued TABLE 12 Shepard Winslow - - - - 1 5 2 7 3 2 3 4 9 2 5 8 17 13 91 17 65 78 Rosenstock Beaver Mouse Eastern Fox Squirrel MiceA/oles Rodents Muskrat Mammals, continued Squirrel Porcupine Bobcat Felid Dog Red Fox Mountail Lion Gray Fox Fox Mink Opossum Canid Longtail Weasel River Otter Striped Striped Skunk Black Bear

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. - Barrack - 1 1 - - 77 22 1 3 168 39 671 2970 138 150

- 4 Continued TABLE 12 69 99 Shepard Winslow Hughes Keyser Farm Shepard 1 1 2 8 10 156 158 9626 Rosenstock Mammals, continued Raccoon Mustelid Elk Large Carnivore Small Small Carnivore White-tailed Deer Cervid Carnivore

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. ------7 Barrack ------29.6 3.2 29.6 3.2 ------+ + + + + + 4.6 Hughes Keyser Farm Shepard - - .2 .2 .1 20 ------2 2 19.8 4.6 TABLE TABLE 13 --- + + + + ++ - - - - - + + + + + + + + - - - .2 .1 PERCENT OF TOTAL NISP BY SITE 6.9 6.6 7.2 5.5 4.4 4.5 11.3 Rosenstock Shepard Winslow Bullfrog Reptiles Frogs/Toads Eastern Painted Turtle Eastern Spiny Softshell Eastern Box Turtle Box and Pond Turtles Lizards Poisonous Snakes Non-poisonous Snakes Birds Mergansers Snake Common Musk Turtle Coral Snakes Snapping Turtle Common Loon Geese Turtle Amphibians .3 Whistling Whistling Swan

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. ------.3 Barrack ..------3 1.6 ------1 + + .2 ------.1 .1 .3 .2 .1 1.7 Winslow Hughes Keyser Farm Shepard ------Continued TABLE TABLE 13 .3 -- - + + + + + + + + + + + + + + + .8 3.8 .2 3.6 Rosenstock Shepard

Ruffed Ruffed Grouse Birds, Birds, continued Red-Tailed Hawk Common Bobwhite Passenger Pigeon Pileated Woodpecker Red-Bellied Woodpecker Blue Jay Fishes Perching Perching Birds Pintail Common Grackle Wild Wild Turkey Creek Chub River Chub Big Mouth Chub Suckers Owl Woodpeckers Common Shiner American Crow American Eel

Q. with permission of the copyright owner. Further reproduction prohibited without permission. .3 .3 .3 89.6 Barrack + + .2 .1 .3 75.2 90.6 59.1

Continued TABLE 13 92.5 30.4 .5 Shepard Winslow Hughes Keyser Farm Shepard - + + + + + + + + + + + + + + + + + + .1 82.4 Rosenstock

Northern Hog Sucker Shorthead Redhorse Redhorse Suckers Fishes, continued Brown Brown Bullhead Striped Bass unfishes S Minnows Perch-like Fish Catfishes Bony Fishes Mammals Golden Redhorse Sturgeon Eastern Cottontail Silver Redhorse Eastern Chipmunk White Sucker Snowshoe Hare (Jackrabbit) Eastern Gray Squirrel Woodchuck Trouts and Allies

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 175 ------.3 .3 Barrack Shepard ------.3 .3 Keyser Farm ------+ + + + + + + + + + + + .2 .1 ------2 .1 .1 .1 .1 .2 .2 .2 .3 .2 .1 .2 .1 .1 2.6 8.4 Winslow Hughes ------Continued TABLE TABLE 13 .6 .3 .3 1.7 3.2 ------+ ++ + - - - - - + + - + + + + - + - + + + + .2 .6 .1 .6 .2 Rosenstock Shepard

Eastern Fox Squirrel Mammals, continued Rodents Mice/Voles Muskrat Squirrel Beaver Mouse Porcupine Mountail Mountail Lion Bobcat Felid Dog Red Fox Gray Fox Fox Black Bear Opossum Striped Striped Skunk River Otter Canid Longtail Longtail Weasel Mink

with permission of the copyright owner. Further reproduction prohibited without permission. - - .3 Barrack Shepard - ---- .3 Keyser Farm -- - - .2 .1 .3 .8 13.8 41.2 40.1 - - 9.8 4.5 Winslow Hughes ------Continued TABLE 13 20 1.2 + + + + + .3 .3

19.4 28.7 39.1 Rosenstock Shepard Mammals, continued Large Carnivore Mustelid Raccoon Elk Cervid Small Carnivore + = taxon present but less than .1% of total assemblage Carnivore White-tailed Deer - = taxon not present in assemblage

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 177

consisted of finding the most abundant element for each species taking into

account both side and portion of the bone (i.e., left proximal tibia or right distal

humerus). The total MNI for each class of animals was then calculated by

adding the MNIs for each species or family of animal (Table 14 and Table 15).

One of the problems encountered when calculating MNI is taphonomic.

As discussed above, some elements are more susceptible to taphonomic

forces. This variability in breakage can affect the estimated MNI with more

fragmented bones potentially resulting in a higher MNI if those fragments are

identifiable. Some elements, such as the distal humerus, have many

identifiable features which could lead to this result. With many elements,

however, increasing fragmentation makes them even more difficult to identify

thereby resulting in a lower MNI. Indeed, as Marshall and Pilgram concluded:

While MNI decreases with increasing fragmentation, NISP moves in two directions with fragmentation, increasing at low levels of fragmentation and decreasing at high level of fragmentation. In addition, MNI appears more sensitive than NISP to the relative identifiability of different body parts. We believe MNI may be a less representative descriptor of relative element frequency than NISP in highly fragmented assemblages (Marshall and Pilgram 1993:261).

Unfortunately, Marshall and Pilgram do not define what they mean by

"highly fragmented," leaving it to the researcher to make that determination. If

the assemblages from this study are compared to each other, then the two

primary assemblages are highly fragmented and the secondary assemblages

are the less fragmented (see Chapter Three for a more detailed discussion of

the fragmentation of these assemblages). While most of this is due to

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. ------1 Barrack ------1 1 1 1 1 ?? 3 3 11 3 Hughes Keyser Farm Shepard ------1 1 1 2 3 8 Winslow ------? 2 TABLE TABLE 14 Shepard --- 1 1 1 1 1 1 1 1 1 2 9 ? ? 2 5 3 9 17 42 MNI FOR IDENTIFIABLE REMAINS BY SITE Rosenstock Frogs/Toads Reptiles Bullfrog Box and Pond Turtles Lizards Eastern Box Turtle Common Musk Turtle Eastern Painted Turtle Eastern Spiny Softshell Snapping Turtle Birds Poisonous Poisonous Snakes Coral Snakes Non-poisonous Snakes Mergansers Snake Common Loon Amphibians 18 Geese Turtle Whistling Whistling Swan

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Barrack 1 1 1 1 4 Continued TABLE TABLE 14 Shepard Winslow Hughes Keyser Farm Shepard - 1 1 1 1 1 1 1 1 1 1 1 1 3 3 3 7 16 23 56 Rosenstock

Pileated Woodpecker Red-Bellied Woodpecker Birds, Birds, continued Red-Tailed Hawk Ruffed Grouse Big Big Mouth Chub Blue Blue Jay Pintail Common Bobwhite Passenger Pigeon River Chub Fishes Perching Birds Common Grackle Suckers Wild Wild Turkey Woodpeckers Creek Chub Common Shiner Owl American Crow American Eel i with permission of the copyright owner. Further reproduction prohibited without permission. 14 Barrack 20 1 2 Continued TABLE TABLE 14 45 77 45 Shepard Winslow Hughes Keyser Farm Shepard - - 1 1 1 1 1 1 1 1 1 1 2 3 6 4 3 3 9 4 129 Rosenstock

Northern Hog Sucker Fishes, continued Brown Bullhead Minnows Redhorse Suckers Shorthead Redhorse Bony Bony Fishes Perch-like Fish Golden Redhorse Silver Redhorse Striped Bass Sunfishes Eastern Cottontail Eastern Chipmunk Catfishes Sturgeon Mammals White Sucker Eastern Gray Squirrel Snowshoe Hare (Jackrabbit) Trouts and Allies Woodchuck

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Barrack 1 1 1 1 2

1 1 1 2 3 2 4 - - 1 1 4 1 1 1 1 4 2 2 4 1 Continued TABLE TABLE 14 Shepard Winslow Hughes Keyser Farm Shepard ------1 1 1 1 1 1 1 1 1 2 2 7 4 2 3 Rosenstock Beaver Mouse MiceA/oles Porcupine Red Fox Rodents Muskrat Dog Mammals, continued Longtail Longtail Weasel Mountail Lion Bobcat Felid Eastern Fox Squirrel Squirrel Fox Mink River Otter Black Bear Opossum Gray Fox Canid Striped Skunk

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Barrack 1 1 3 4 1 1 19 17 7

1 4 4 13 Continued TABLE 14 29 28 Shepard Winslow Hughes Keyser Farm Shepard Rosenstock

Raccoon Mustelid 10 Elk Small Carnivore Large Carnivore 4 Cervid Carnivore White-tailed Deer 69

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. ------6.3 Barrack Shepard ------? 13 ------? 3 18 1.6 1.6 1.6 1.6 4.9 Hughes Keyser Farm ------1.1 1.6 1.1 1.1 2.2 3.4 Winslow ------? TABLE TABLE 15 4.3 9 Shepard - ? 9 ? .7 .4 .4 .4 .4 .4 .7 .4 .4 .4 .4 1.1 1.9 3.4 PERCENT MNI FOR IDENTIFIABLE REMAINS BY SITE Rosenstock Frogs/Toads Bullfrog Reptiles 6.5 Eastern Spiny Softshell Snapping Turtle Common Musk Turtle Eastern Painted Turtle Eastern Box Turtle Box and Pond Turtles Non-poisonous Snakes Lizards Poisonous Snakes Mergansers Coral Snakes Snake BirdsCommon Loon 16 Turtle Amphibians 6.9 Geese Whistling Whistling Swan

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Barrack 1.6 1.6 - 6.3 1.6 1.1 1.1 2.2 Continued TABLE TABLE 15 4.3 4.5 11.5 13 6.3 Shepard Winslow Hughes Keyser Farm Shepard - .4 .4 .4 .4 .4 .4 .4 .4 .4 .4 .4 .4 1.1 1.1 1.1 8.8 6.1 2.7 21.4 Rosenstock

Passenger Pigeon Birds, Birds, continued Red-Tailed Hawk Ruffed Grouse Perching Perching Birds Pileated Woodpecker Red-Bellied Woodpecker Blue Jay Pintail Common Bobwhite Big Big Mouth Chub River Chub Fishes Creek Chub Common Grackle Common Shiner Suckers Woodpeckers Owl Wild Turkey American Crow American Eel

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 1 6.3 6.3 87.5 Barrack 1.6 1.6 6.6 73.8 87 1.1 2.2 2.2 Continued TABLE TABLE 15 2.1 95.7 86.5 Shepard Winslow Hughes Keyser Farm Shepard - - .7 .4 .4 .4 .4 .4 .4 .4 .4 .4 .4 1.1 1.5 1.5 1.1 1.1 2.3 3.4 49.2 Rosenstock

Fishes, continued Redhorse Suckers Brown Bullhead Minnows Perch-like Fish Northern Hog Sucker Shorthead Redhorse Silver Redhorse Golden Redhorse Striped Bass Sunfishes Bony Fishes Mammals Catfishes Sturgeon Snowshoe Hare (Jackrabbit) Eastern Cottontail Eastern Chipmunk White Sucker Eastern Gray Squirrel Trouts and Allies Woodchuck i I

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. - - - - - . - - 6.3 6.3 Barrack Shepard ------. ------1.6 1.6 1.6 3.3 - - 1.1 1.1 1.1 1.1 1.1 1.6 1.1 3.3 1.1 1.6 1.1 4.5 2.22.2 1.6 1.6 4.3 6.3 3.4 4.5 4.5 3.3 Winslow Hughes Keyser Farm ------Continued TABLE TABLE 15 2.1 8.5 ------.4 .7 .4 .4 .4 .4 4.3 .7 .7.4 2.1 .4 .4 .4 2.1 1.1 2.7 2.1 Rosenstock Shepard

Squirrel BeaverMuskrat 1.5 Eastern Fox Squirrel Mouse Mammals, continued Porcupine Mountail Lion MiceA/oles Rodents Bobcat Felid Dog Red Fox Opossum Gray Fox Fox Longtail Weasel Mink River Otter Striped Skunk Canid Black Bear

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. - - 6.3 6.3 43.8 Barrack - -- 73.9 Keyser Farm Shepard ------6.6 4.3 31.1 Hughes - - “ 4.5 14.6

Winslow - Continued TABLE 15 8.5 2.1 61.7 31.5 4.9 4.3 MNI for site ------1.5 26.3 Rosenstock Shepard RaccoonMustelid 3.8 Elk Large Carnivore Cervid Small Carnivore Carnivore White-tailed Deer - = taxon not present the in + assemblage= taxon present but less than .1% of total

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 188

collection strategy, the cause of fragmentation does not matter for determining

the appropriateness of using MNI or NISP, only the resulting degree of

fragmentation itself. Although some statistical tests used in this study, such as

the Shannon-Weaver Index for Evenness and Richness, require the use of MNI

rather than NISP, others can be performed using either calculation. Because

the primary assemblages are more fragmented, this would indicate that NISP

would be more appropriate to use when possible. For this reason, for those

tests where using either NISP or MNI is optional, NISP will be used. This

extends the use of the conclusions reached by Marshall and Pilgram from

element frequency to taxa frequency. While their conclusions were reached by

testing the accuracy of the different calculations at an element level, because

NISP as defined for this research only counts those bones or bone fragments in

a given taxon that can be identified to element, combining element NISPs into

taxon NISPs should yield similar conclusions.

A second problem in calculating MNI is that some bones have a larger

number of identifiable features on them, making a larger proportion of the

fragments identifiable to element. A high MNI estimate can then result if those

elements are used for calculations. Conversely, using elements without as

many easily identifiable features when estimating MNIs can result in low

calculations. For example, with distal humeri, even relatively small fragments

can be identified to element because of the number of distinctive features of the

bone.

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 189

A third problem in calculating and interpreting MNI is that the calculation

of the MNI figure is an interpretive exercise and as such different researchers

can have different figures for the same assemblage depending on which factors

they take into account in their calculations. For example, if an assemblage

contained three left proximal humeri, two left distal humeri, and four right

proximal humeri an MNI of five would be calculated if side was used as the only

determining factor. An MNI of four, however, would be obtained if both side

and elemental portion were used as determining factors. Explicitly stating the

criteria used for calculating MNI becomes important when interpreting these

figures and comparing them to assemblages from other sites. As stated above,

for this study, MNI was calculated taking into account both side and element

portion. The pros and cons of using MNI and NISP have been discussed at

great length in the zooarchaeological literature (see Binford 1981, Grayson

1984, and Lyman 1993 for some of the more recent examinations of these

calculations) which can be consulted for further discussion.

MNE

MNE represents the Minimum Number of Elements that are needed to

account for a defined sample of specimens. MNE differs from MNI in that MNE

is calculated for each element separately, rather than being calculated for a

complete individual. MNE can be used to address a number of different

questions including animal processing or element deposition away from the site,

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variability in taphonomic forces on different elements, and variable use of

different body parts. In this study, MNE was calculated for deer for postcranial

elements using both side and elemental portion data. In addition, MNE for long

bones was calculated separately for proximal and distal ends (Table 16). By

calculating MNE figures separately for different parts of a single element, the

"E" in "MNE" no longer refers to a complete element but rather a portion, such

as proximal or distal end, of an element as defined by the analyst. In this

study, MNE refers to a complete element if no further delineation of portion is

listed [i.e., astragalus). MNE refers to a partial element only where a portion is

defined [i.e., distal tibia). Although it may be confusing to have one term refer

to either a complete or partial status of an element, it would be more confusing

to use a new term when a partial versus a complete element is being

discussed.

Because MNE is calculated on an element by element basis, the

individual MNE figures can be combined to examine use of larger body parts

such as forelimb or axial elements. For interpretive purposes, the MNE of a

complete deer skeleton was calculated and divided into larger body parts of

forelimb, hindlimb, unspecified lower limb [i.e., metapodials, phalanges, etc.)

and axial. The same list of elements was used when calculating the MNEs for

the complete deer as were used for the archaeological sample even though the

complete deer assumes complete elements. For example, when the proximal

and distal ends of an element were counted separately in the archaeological

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. ------1 3 2 5 5 12 28

- _ ------Farm Barrack -- 1 1 2 3 2 5 2 6 4 7 1 15 14 1 46 TABLE TABLE 16 - - - - - 1 1 8 3 4 10 15 (ODOCOILEUS VIRGINIANUS) ------1 1 4 1 1 1 20 14 1 2 7 7 43 139 16 - - 1 8 6 MINIMUM NUMBER OF ELEMENTS (MNE) FOR DEER 12 15 22 61 24 28 22 20 71 72 120 531

Rosenstock Shepard Winslow Hughes Keyser Shepard 1st 1st Carpal Forelimb Forelimb Elements Proximal Proximal Radius Prox. Metacarpal Forelimb Total Inter. Inter. CarpalRadial Carpal 13 Scapula Distal Ulna Prox. Prox. Humerus Distal Humerus Distal Radius Proximal Ulna Distal Metacarpal 36 3rd 3rd Carpal Ulnar Carpal 2nd Carpal 2nd/3rd Carpal 4th Carpal Access. Carpal

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Continued

Rosenstock Shepard Winslow Hughes Keyser Shepard Farm Barrack

Hindlimb Elements Proximal Femur 49 1 4 12 - 3 Distal Femur 74 - 6 14 - 2 Proximal Tibia 111 3 8 17 1 2 Distal Tibia 67 1 6 9 - 4 Patella - - 1 2 Prox. Metatarsal 115 5 9 28 31 3 - Distal Metatarsal 22 1 8 4 - 1 m Calcaneous 75 1 16 16 - 7 Astragalus 67 - 8 21 - 5

Lateral Maleolus - - 1st Tarsal -- 2nd/3rd Tarsal 10 - 7 2nd Tarsal 11 - 1 3rd Tarsal - - Central/4th Tarsal 43 - 3 7 - 3

Hindlimb Total 644 12 69 138 32 30

UnsDecified Limb Elements Metapodial 86 1 27 1 1 1st Phalanx 126 7 10 37 - 8 193 - - 1 3 3 4 7 12 13 Shepard Barrack ------1 37 Farm -- 2 2 6 4 4 2 1612 1 9 13 80 38 106 1 Continued TABLE 16 - 7 26 2 16 2 7 12 6 7 3 8 8 16 13 33 Winslow Hughes Keyser ------1 1 1 2 39 9 19 4 142 191 16 18 49 53 24 20 66 27 50 108 108 352 645 Rosenstock Shepard Unspec. Limb Total Maxilla Mandible Hyoid Lumbar Vertebra 3rd 3rd Phalanx Pelvis 2nd Phalanx 91 Cervical Vertebra Caudal VertebraSternum 4 11 Sacrum Rib Axis Thoracic Vertebra 140 Axial Elements Atlas Axial Axial Total

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 194

sample, they were also counted separately in the complete deer even though in

the complete deer they would be together in a single element. This results in

similar data categories for comparing assemblages from both skeletally

complete and archaeological contexts.

Because calculating MNE, as with calculating MNI, requires that the

analyst define a set of criteria under which the calculations are performed, MNE

has some of the same problems as MNI. Varying the number of differentiating

criteria (i.e., element portion, side, etc.) used in calculating the figure can yield

very different results. Using few criteria can result in overestimates for both

MNE and MNI while using a large number of criteria can result in

underestimates for these calculations.

Diversity

Diversity, as used here, refers to the variety of taxa represented in each

faunal assemblage. Diversity will be examined primarily at two levels - class

and species. This will be done to determine not only if particular species of

animals within a class were preferred (i.e., turkeys instead of swans) but also if

whole classes of animals were preferred. This differentiation of distribution of

species and classes of animals between sites will be one of the key data sets

for describing hunting patterns. Important information related to the distribution

of species will be the seasonal behavioral and distributional changes in the

animals, as well as the habitats that they occupied.

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 195

Fifty-three species from 36 families were recovered at the sites under

examination (Appendix 1). The number of species recovered from each class

varied and consists of one species (two families) of amphibians, five species

(six families) of reptiles, 12 species (10 families) of birds, 12 species (seven

families) offish, and 23 species (11 families) of mammals. These animals

occupied a variety of habitats (Appendix 2). The varieties of these habitats and

the changes in the distribution of various species among them throughout the

year can be important when interpreting hunting strategies. For example, elk

migrate up mountains in spring and down into the valleys in the fall (Burt and

Grossenheider 1980:215). Male elk generally shed their antlers in February or

March so if the season of kill can be determined, the habitat where they were

killed can be inferred, possibly yielding information about hunting patterns and

ranges. Migrating birds are another example of the importance of knowing

habitats and ranges of each species. Many migrating birds are only in the

Potomac Valley area for limited times of the year and this information can be

used to infer seasonality of hunting (Burt 1980).

Because of the problems of sampling and representativeness associated

with some of the assemblages discussed in Chapter Three, the two primary

assemblages, those from the Rosenstock (18FR18) and Hughes (18M01) sites,

will be used for the principle interpretations of hunting patterns for the

Montgomery Complex and the Luray Focus. Data from the associated

secondary assemblages will be compared to that from the primary assemblages

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but will not be used as sole data for any argument. Data from secondary

assemblages will be used as supporting or contradictory evidence are

insufficient to make important statements.

There are many ways of measuring diversity both within an assemblage

and between assemblages. No method of quantifying data, however, is

appropriate for every research question. After an examination of both statistical

and zooarchaeological literature, several measures have been chosen for this

analysis. These measures can be used at different levels depending on the

research question. How they are being used here will be described below.

Shannon-Weaver Index

Evenness

The Shannon-Weaver index measures the certainty with which a

randomly selected remains can be identified to a given taxon (Popper 1988).

Another way of phrasing this is that the index measures the evenness of the

distribution of individuals across all of the taxa in a given assemblage.

If there are many taxa evenly distributed in the assemblage, the certainty of predicting the identity of the selected plant is low and the index indicates high diversity. If the taxa are few and unevenly distributed, the index indicates low diversity (Popper 1988:66).

The formula for calculating this measurement is H= -E(MNI in taxon/total

MNI) loge(MNI in taxon/total MNI) (Grayson 1984:158-159). As can be seen in

the formula, the index is MNI based and incorporates the relative abundance of

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 197

each taxon to determine this evenness. For all following calculations using this

formula, only MNIs calculated at the genus level or better were used.

There are two conditions of an assemblage which can skew this

measurement. The first of these is uneven distribution across taxa within an

assemblage. If there is an uneven distribution of MNIs among taxa, the index

will reflect a lower diversity than is the case. The second condition which can

skew results is a low MNI in each taxon. Pearsall (1983:130) recommends that

counts (or MNIs) per taxon of more than 10 are needed to give accurate

results. Although both Pearsall and Popper discuss the limitations and

requirements for calculating this index using data from ethnobotanical analyses,

the same restrictions hold when applying this statistic to zooarchaeological

remains.

As will be seen in Chapter Five, at the genus level both of the primary

assemblages suffer from one or both of the skewing conditions mentioned

above. Both the Hughes and Rosenstock site assemblages are relatively

uneven in the distribution of MNI between taxa with a wide range of MNIs

among the taxa. Both assemblages also have taxa with less than 10 MNI. For

these reasons, the Shannon-Weaver Index cannot be calculated on these

assemblages at a genus level. If, however, MNIs are calculated on the genus

level and then combined at the class level the total MNIs by class increase

sufficiently to result in more accurate diversity calculations. For these reasons,

this index will be used at the class level. By calculating the index at this level,

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 198

the diversity of the number of taxa represented is no longer included in either

the calculation or the interpretation of the index. Instead, the evenness of

distribution among classes is calculated and the use of whole classes of taxa is

examined. Although this is a broad level of analysis, it is the only taxonomic

level at which all of the requirements for the calculation of the Shannon-Weaver

Index are met.

Richness

"In studies of taxonomic richness, analysis is focused on the number of

taxa, often species, that have contributed to a faunal assemblage, and on

comparing assemblages on the basis of the number of taxa they contain"

(Grayson 1984:132). The Shannon-Weaver Index can be used to address this

taxonomic richness, as well as the evenness of distribution of individuals among

those taxa as described above. Richness is calculated by dividing H (see

above) by the natural log (loge) of the total number of taxa represented (Reitz

via Lev-Tov, personal communication 1993). If diversity were being calculated

at the genus level in the present analysis, only taxa which were identified to the

level of genus or better would be counted. The Hughes site would then have

twenty-three taxa and the Rosenstock site would have fifty-seven taxa resulting

in divisors of twenty-three and fifty-seven, respectively (see subsequent data

presentation in Chapter Five). Since this measure is being calculated at the

class level for these assemblages however, the divisor for these sites is four for

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 199

the Hughes site (reptiles, birds, fishes, and mammals) and five for the

Rosenstock site (amphibians, reptiles, birds, fishes, and mammals). Note that

MNI is not calculated originally at the class level but is calculated at the genus

or species level and then summed by class. The number of classes

represented are then counted as the divisor for richness rather than counting

genus or species. As with the calculation for evenness, richness is no longer

being addressed with the number of taxa represented at the genus level but

rather is being examined with the number and relative frequency of taxa at the

class level.

Chi-Square

There are two versions of chi-square tests. The first is a one-sample

test "in which a sample is compared to a specified theoretical population and a

test is made of how good the correspondence or 'fit' is between these two

distributions; the idea is clearly important when we are testing theoretically-

derived models" (Shennan 1988:65). The second version of this test is the chi-

square test for cross-classified data. In this second version, rather than

comparing a sample to a theoretically-derived population, samples are

compared which have been classified by two different criteria. It is the second

version that will be used in this analysis since the samples being used have

been classified in two different ways - by archaeological complex (each

represented by a primary site assemblage) and by taxonomic class.

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 200

Calculating chi-square allows one to test an hypothesis that the

distribution of specimens across classification categories is the same (the null

hypothesis) or different. After chi-square is calculated, it is then compared to

the value in the chi-square table for the required level of significance. If the

calculated value of chi-square is greater than the tabulated value then we can

reject the null hypothesis. Note that chi-square does not measure the strength

of the relationship examined, just whether or not a relationship exists (Shennan

1988:70-74). Chi-square is sensitive to sample size and if a sample is very

large then the chi-square value will be correspondingly large. Therefore, once

the minimum value has been reached for a given confidence level, a very high

chi-square value does not indicate any stronger a relationship than one close to

the minimum value required.

There are two requirements for calculating this test. The data must be

on at least a nominal scale and there must be no expected frequencies less

than one and there should not be more than 20% of the cells with expected

values less than five (Norusis 1989:160). When the two samples being

considered are organized by class using MNI, the Hughes site has a high

frequency of low MNIs (see presentation of data in Chapter Five). One way of

alleviating this problem is by using NISP instead of MNI. For this reason, the

chi-square values will be calculated using NISP figures rather than MNIs.

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Kolmogorov-Smirnov

The Kolmogorov-Smirnov test examines the significance of difference

between two assemblages or whether or not the differences between two

assemblages are significant at a given level. This test assumes that the

assemblages represent random samples of the archaeological record. The

Kolmogorov-Smirnov test then examines the difference between the distribution

of relative frequencies among categories to determine whether or not the

samples came from similar populations. As discussed by Grayson

... two samples can differ greatly in the relative abundances of the taxa that they share, but not differ significantly in their cumulative distribution functions. Such a result suggests that there may be some underlying structure in the relative proportions of species represented in a pair of faunal assemblages that is independent of the specific species involved (Grayson 1984:155).

It is the Kolmogorov-Smirnov test that will be used to examine that underlying

structure of population similarity or dissimilarity. Thus, while a chi-square

analysis will examine the significant differences in the relative abundances of

specific species within the assemblages, Kolmogorov-Smirnov examines the

"underlying similarity in the structure of the species-abundance distributions of

these two faunal assemblages, one that is independent of the species involved"

(Grayson 1984:156). Because chi-square takes into account the actual taxa

involved in the distributions, it can indicate a significant difference because of

uneven distributions by taxa. Kolmogorov-Smirnov bypasses that potential

skewing by examining the cumulative frequencies which will not be affected as

strongly by individual taxa distributions.

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There are two steps needed to calculate and evaluate significance of the

Kolmogorov-Smirnov test. The first of these requires calculating the cumulative

relative frequencies of specimens in each category for each assemblage. In

the present case, this is the distribution of specimens (NISP) for each class for

the two primary assemblages, Hughes and Rosenstock. The differences

between the cumulative frequencies is then calculated and the greatest

difference is noted. The second step is to calculate the figure for which the

observed greatest cumulative frequency difference represents a significant

difference in the populations from which these samples were taken. If the two

populations are different then there is a theoretical difference within which any

random sample from those populations should fall. "If the observed difference

is equal to or greater than this then it is statistically significant at the set level"

(Shennan 1988:60-61). This theoretical difference at the 0.05 confidence level

is calculated by using the formula 1.36/n1+n2/n1n2 where n1 equals the number

of specimens in sample one and n2 equals the number of specimens in sample

two. To calculate this figure at the 0.01 confidence level substitute 1.63 for

1.36 in the formula above and at the 0.001 confidence level substitute 0.195.

If we hypothesize that two populations are different then our goal is to

reject the null hypothesis that there is no difference between the two

populations. The minimum theoretical difference for that hypothesis to be

rejected is the figure calculated in the second part of the Kolmogorov-Smirnov

test. If the figure observed by calculating the greatest cumulative frequency

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difference in part one of the test is less than the figure in part two of the test

then one cannot reject the null hypothesis. If the figure from part one is equal

to or greater than the figure in part two then one can reject the null hypothesis

at the confidence level chosen for the calculation (Shennan 1988:53-61).

Summary

The analytical techniques described above provide a range of data that

can be used to address questions of species diversity, seasonality,

completeness of individuals, age of individuals, and general demographic

characteristics of the various assemblages. These, in turn, will be used in the

following chapters to address the broader cultural historical and theoretical

questions discussed in previous chapters, including issues of sociocultural

change and complexity and their interaction with economic strategies and the

adaptation of these strategies to changing sociocultural contexts.

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SUMMARY OF DATA

Introduction

This chapter presents the data needed to address the research questions

defined in Chapter One. Data will be presented for each individual site and will

be used to interpret animal utilization patterns and strategies at the sites.

Comparisons will then be made between sites within the two archaeological

complexes under question as well as between both complexes. These

comparisons will be made using the analytical methods defined earlier.

Calculating the figures of NISP, MNI, MNE, etc. on a site-by-site basis will

provide the data necessary to make conclusions about patterns in the data. In

addition, these observations will be tested statistically to confirm their empirical

validity. Before this is done, however, it will be necessary to determine what

types of data can and should be used to address the research questions.

Among the specific questions being asked by this research are the

following: what were the hunting strategies during each of the two periods in

question; did these strategies change over time; and, if these strategies did

change, what are some of the possible reasons for this that current site

204

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evidence supports? Several types of data are needed to examine and define

these hunting strategies. These data include: species diversity (which animals

were being hunted); what proportions of different animals were being hunted

(i.e., more fish, fewer birds, etc.); the types of environments these animals lived

in; what season of the year these animals were being hunted; and whether or

not certain ages and/or sexes of individual species were preferred.

An additional associated question to be addressed is how were the

animals processed prehistorically both in the field and back at the village? The

examination of white-tailed deer remains will yield the primary data to address

this question. As will be illustrated below, deer are the most ubiquitous species

in the assemblages from all of these sites. Field preparation after hunting will

have had an effect on the distribution of deer elements recovered at the village

site, and this may be evident in the assemblage. One simple example could be

that if non-meat bearing parts such as the head and lower limbs were removed

in the field to lighten the load being brought back to the village, then these

skeletal elements will not be in the site assemblage. The distance of hunting

away from the site will also affect the distribution of skeletal elements with more

complete field dressing performed the farther away from the site the kill was

performed. The techniques used in processing the meat at the site will also

have had an effect on the assemblage. Skeletal part distribution, fragmentation

patterns, and the location and types of butchering scars will be used to briefly

examine butchering and processing techniques. The results from answering all

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of these more specific data-oriented questions will be used to address the

implications for the larger issues of sociopolitical complexity, sedentism, etc.

that have been defined in Chapter One.

Animal Utilization at Montgomery Complex Sites

Diversity

The assemblage from the Rosenstock site is the only primary

assemblage for this complex. It has a wide variety of animals with at least two

different amphibians, at least eight species of reptiles, 14 identified species plus

one additional family of birds, 13 species and five additional families offish, and

25 species of mammals (Table 12). Although the MNI for many of these

species is low (Table 14), they represent a wide variety of animal species.

Because flotation material was not available for this analysis, all distributions

and conclusions here are based only on screened material. Small remains

found in flotation samples typically include the classes least represented here

(i.e., fish, birds, etc.). This potential bias will be taken into account and

discussed in the interpretations both for the site and its comparison to other

sites.

Identifiable remains were distributed very unevenly among the classes

identified in the assemblage. Mammals represent the greatest proportion of

remains with 82% of the NISP (Table 13). Bird and reptile each represent

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seven percent of the NISP, fish are four percent and amphibians are less than

one percent. As can be seen with this distribution, although mammals were the

most heavily utilized class, there was still variety in the classes of animals being

collected.

Deer are the most ubiquitous species recovered from the Rosenstock

site. Sixty-seven percent of the remains identifiable to the level of family or

better are white-tailed deer (Odocoileus virginianus). In addition, deer comprise

93% of the mammals that are identifiable to the level of family or better. Turtles

are the next most frequent remains with 23% of remains identifiable to the level

of family or higher being turtle. It is possible that this is a disproportionately

high percentage of NISP for turtle. Most of the turtle specimens identified were

carapace or plastron fragments. Although efforts were made to reconstruct

fragmented carapaces and plastrons, few mends of pieces broken in antiquity

were made. Because one carapace or plastron can easily break into many

pieces depending on the degree of fusion and post-depositional deterioration of

the fragments, the NISP value may be high because of these taphonomic

forces.

An additional factor that could be misleading in the use of turtle

carapaces in estimating dietary remains is that a turtle carapace can be

collected after the turtle has died. These carapaces can be used for many

purposes, none of which represent a dietary contribution by the individual turtle

that the carapaces could represent. This same problem is encountered with

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deer antler. Because deer antler are shed every year, deer antler could have

been frequently collected throughout the area. These antler would not

represent an individual in the diet. Because of this, deer antler are not used as

elements for any MNI or dietary contribution estimates. Because turtle MNIs

were calculated using skeletal elements rather than carapace and plastron

fragments, the number of skeletal elements is probably a more reliable estimate

of the actual proportions of turtle used at the site.

Turkey constitute three percent of the NISP, raccoon and elk each are

one percent and all other species in all classes each represent less than one

percent of the identifiable assemblage (Table 13). In rank order then, the most

frequently collected animals were deer, turtle, turkey, raccoon, elk, and all

others. This does not necessarily equal the rank order of the contribution of

meat by animal. When body size and available meat weight per animal is

taken into account, this order changes to deer, elk, turkey, turtle, raccoon, all

others. Because most of the species in this assemblage have an MNI lower

than 10, meat weight estimates were not calculated. In some archaeological

assemblages, the relative value of certain species can be underestimated or

overestimated because of varying body sizes between species. For example,

in an assemblage with one deer and 100 fish, estimating the meat weight that

each species would have contributed to the diet would show that although the

MNI for fish was 100 times that of deer, each species could have contributed

the same amount of meat. This would give a much different interpretation than

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if you did not take into account the size and meat available from each individual

was not taken into account. For the Rosenstock assemblage, however,

because so many of the species have such low MNIs (especially the smaller

species), I did not feel that calculating the meat weights for each species would

change the ranking of the importance of species in the diet except in very few

cases (such as elk as seen above).

The Rosenstock site is located in a forested mountainous region of the

Central Maryland Piedmont immediately above the banks of the Monocacy

River. Because of this location, both terrestrial and freshwater aquatic species

were immediately available to the inhabitants of the site. Indeed, all of the

terrestrial species in this assemblage routinely occupy a forested habitat,

whether mountainous or not. Elk migrate up mountains in the spring and down

to valley areas in the fall. They would potentially be available to the residents

of the Rosenstock on a year-round basis. Hunters could go slightly farther up

into the mountains in the spring/summer, wait for the elk to move when they are

fattest and most productive for meat purposes in the fall, or could go further

down the valley if necessary in the winter if elk were desired. Either way,

because of the central location of the site in this distribution of areas, elk could

probably have been hunted throughout the year.

The aquatic species recovered at the site occupy a variety of riverine

habitats (Appendix 2). These habitats range from quickly flowing water as

would be found directly in the river to small pools and shallow areas along the

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river's edge, to brackish closed areas that would occur either after flooding or

heavy rainfall further away from the water's edge. The occupants of the

Rosenstock site were exploiting faunal resources in all of these habitats and

were not limiting themselves to certain species of animals or specific habitats.

This further supports the idea that the occupants of the Rosenstock had a

broad-based subsistence system, one that took advantage of the many diverse

resources available to them. They were not simply coming to the area for a

particular resource (such as migrating elk or spawning fish) but were collecting

from all habitats in the area.

While some of the birds recovered in the assemblage are migratory birds

and live further north for parts of the year, all of the birds not normally found in

the immediate vicinity of the site do migrate past the site area at some time of

the year. Because the normal range for these birds can be up to 1000 miles

north of the site, it can be assumed that these birds were hunted only while

migrating and were not hunted by traveling great distances. A list of these

species as well as the time of year that they would have been in the site area

and the implications of their presence in the assemblage will be discussed

below in the section on seasonality.

All but two of the aquatic species can be found in medium-sized rivers or

the pools and shallow areas alongside the river. The two exceptions to this are

the American Eel, Anguilla rostrata, and the Striped Bass, Morone saxatilis.

The American Eel is a catadromous species - one that spend most of its life in

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fresh water but travel to the sea to spawn. It is more common near the sea

and uncommon in more inland streams and lakes. The modern distribution of

the American Eel does not extend into the immediate site vicinity. The Striped

Bass is an anadromous species - a marine species spends most of its life in

the sea but that ascends large rivers far upstream to spawn. It can be found in

medium to large rivers, lakes, and connecting rivers during spawning runs.

While the modern distribution of the Striped Bass does not extend into the

immediate site vicinity, it is possible that the prehistoric range of this fish

extended into the Monocacy River. Unfortunately, no data could be found

illustrating the prehistoric distribution of these fishes.

The material from the Winslow site, although not as diverse as that from

the Rosenstock site, still represents a fairly diverse assemblage. Four species

of birds, 16 species of mammals, at least one species of fish, at least two

different reptiles, and at least one amphibian are present in the assemblage

(Table 12). As with many of the assemblages in this analysis, the MNI for

almost all of these species is less than ten (Table 14). The exceptions to this

are raccoon and deer.

For remains identified to the level of class or better 75% are mammals.

The next highest represented class is reptiles at 20%. Birds constitute four

percent of the assemblage with fish and amphibians each making up less than

one percent.

Deer are the largest portion of the remains identifiable to the level of

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family or better at 55%. In addition, deer are 57% of the mammals identifiable

to the level of family or better. Turtles are the next most frequent remains with

22% of remains identifiable to the level of family or better being turtles.

Raccoon represent 11% of all species identifiable to the level of family or better

and 14% of mammals identified at this level. Dog are the next most frequent

species with 12% of the mammals (nine percent of identifiable species for all

classes) being dog. These remains are from a series of dog burials excavated

at the site so these will not be included in any discussions of dietary remains.

It is possible that dogs were used as food so this possibility cannot be ruled out

altogether but these particular specimens do not appear to have been used for

subsistence purposes. Elk comprise seven percent of the mammal remains

identifiable to family or better and five percent of remains identifiable to family

or better for all classes. Beaver are the next most frequently identified species

and are four percent of the mammals identified to the level of family and are

three percent of this level of identification for all classes. Black bear are three

percent of the mammals identifiable to the level of family or better and two

percent of identifiable remains for all classes. Finally, turkey comprise three

percent of remains identifiable to the level of family or better for all classes. All

other species represent less than one percent of the identifiable assemblage

(Table 13).

Although there is a smaller number of species identified at the Winslow

site than at the Rosenstock site, the diversity is still considerable given the fact

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that no screening was performed at this site. At least twenty-seven different

animals were identified. Only five unidentifiable fish fragments were in the

assemblage from this site. This lack of fish may be due to the lack of

screening. As stated earlier, no flotation material was examined for any of the

assemblages in this analysis. All of the fish remains came from 1/4 inch

screens. Even so, the amount of fish recovered for this size screen can be

high as is seen in the Rosenstock assemblage. Even without identifiable fish

remains, however, the Winslow site still has a fairly diverse assemblage. This

is similar to the pattern found at the Rosenstock site - that the occupants of the

sites at this time were utilizing resources from many, if not all, of the habitats in

the area. The Winslow site is located along the banks of the Potomac River

and therefore had access to a variety of both terrestrial and aquatic animals.

All of the species recovered in the assemblage were available in the immediate

site vicinity.

The Shepard site is the final site from the Montgomery Complex

represented in this study. The assemblage from this site is not as diverse as

those from the other sites in this complex and had only 13 different species

represented. How much of this is due to the collection strategies employed at

the site is unknown, but as was discussed in earlier chapters, this sample is

probably not representative of the subsistence remains at the site, and

conclusions regarding overall subsistence patterns cannot be stated using this

assemblage. Instead, the data from this site will be discussed in the framework

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of the hunting patterns of the overall complex as evidenced from the data from

the Rosenstock site and supported by the data from the Winslow site.

The Shepard site assemblage has a total of 345 specimens identifiable

to the level of class or better in this sample. Of these, 323 are identifiable to

the level of family or better. Mammals are the largest proportion of the material

and comprise 92% of the remains identifiable to class and 93% of the remains

identifiable to the level of family. Birds comprise six percent of the remains

identifiable to class and four percent of the remains identifiable to family.

Reptiles are two percent of remains identifiable to class and two percent of

remains identifiable to family (Table 13). No fishes or amphibians were present

in this sample.

MNI figures for this assemblage are low with deer (MNI=29) being the

only species with an MNI greater than five (Table 14). Unlike the species

distribution from other sites in this complex, deer are not the most ubiquitous

species in the assemblage. The Eastern Gray Squirrel has an NISP of 105,

accounting for 35% of the mammal remains and 33% of remains from all

classes identifiable to the level of family. Many of these specimens were

squirrel mandibles that had been part of a necklace. Because of this, the

relative importance of squirrel may be overrepresented in this sample. This is

not to imply that the mandibles are not from individuals that were also used for

subsistence purposes. Instead, it is possible that, because portions of these

elements were used for decorative purposes, the excavators collected what

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may be a more accurate sample of the squirrel at the site whereas other

species were not as well collected because they did not have elements that

showed signs of further utilization.

The next most frequently represented species in this sample is deer.

NISP for deer is 99, comprising 33% of the mammal remains and 31% of

remains from all classes identifiable to the level of family. Raccoon follow deer

in frequency with an NISP of 69. Raccoon are 23% of mammal remains and

21% of remains from all classes identifiable to the level of family. Turkey are

four percent and dog are three percent of the remains from all classes

identifiable to the level of family. In addition, dog constitute four percent of the

mammal remains. Turtle (NISP=7) and the Eastern Fox Squirrel (NISP=6) are

two percent and elk are one percent of the remains from all classes identifiable

to the level of family. The Eastern Fox Squirrel are two percent of the mammal

remains and elk are one percent of the mammal remains identifiable to the level

of family. All other species represented less than one percent of the

assemblage.

The Shepard site is located immediately adjacent to the Potomac River

and was also surrounded by a variety of habitats, each of which could have

yielded a diverse array of animal species. This sample reflects more of the

terrestrial species utilized by the inhabitants of the site than the aquatic species

available. Although, as stated above, this may due to sampling problems and

not because the inhabitants of the site were not collecting aquatic species, this

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cannot be proven given this data.

Seasonality

As discussed in more detail in Chapter Four, there are several ways in

which seasonality of the killing of individuals can be examined. These include

seasonal migration patterns, as well as seasonal behavioral and physical

characteristics, that vary from species to species. For example, the presence

or absence of antler on deer changes throughout the year as antler are shed

and regrown by male deer. The examination of deer crania and whether or not

those crania have their antlers intact or shed indicates the season in which they

were killed. In addition, the examination of mandibular tooth eruption and wear

in young deer occurs at a relatively predictable rate (Severinghaus 1948). The

average birth date is estimated at June 1. Identifying the wear stages of the

mandibles present in the assemblages will yield information that will then

indicate the season in which the individual was killed. Not all of the

assemblages have enough young deer mandibles to address seasonality or

have non-shed antler so the use of these indicators will vary from site to site.

In the following discussions spring includes February, March, and April, summer

includes May, June, and July, fall includes August, September, and October,

and winter includes November, December, and January.

The antler identified in the Rosenstock assemblage contains 13 intact

antlers, antlers which have not been shed from the crania. Since shed antler

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can be collected throughout the area at any time of the year, only intact antler

can be used to indicate seasonality. No crania were identified with antlers

shed. Antlers are present and in velvet from May to September and present

and fully hardened from September to February (Smith 1975:38). All of the

intact antler in the Rosenstock assemblage appear to be fully developed and

tend to be fairly large and nearly complete. Several of the specimens are

complete antlers and range up to 12-15 inches in length. The presence of

these antler would indicate fall/winter hunting of deer.

The seasonality of deer hunting at the Rosenstock site, as evidenced by

the aging of the deer mandibles, indicates that deer were hunted year-round

(Figure 5). Of the 43 mandibles complete enough to be aged, 22 were young

enough to be used to indicate seasonality. Of these 22 mandibles, 50% (n=11)

of them were from the spring, 10% (n=2) were in the summer, 19% (n=4) were

in the fall, and 23% (n=5) were in the winter [see Appendix 3 for an inventory of

all mandible ages and associated data]. Combining the data from the two

indicators (antler and mandibles), it is possible to conclude that although deer

were hunted year-round, the larger older deer, the ones that would have had

the large intact antlers, were hunted primarily in the fall and winter. This

appears reasonable since fall and early winter is the period when deer are at

their peak body weight and would yield the largest amount of meat.

There is no evidence for the seasonality of deer hunting in the

assemblage from the Shepard site. At the Winslow site, however, there were

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

Seasonality of Deer Mandibles 0q.u!\ j jequunN jo S0|qi.puB!/\j <0 218 0 0 □ X CC o c co o o CO o © c CO

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Figure 5 219

15 intact antlers and 24 young deer mandibles. The mandibles are distributed

throughout the year with 33% (n=8) from the spring, 21% (n=5) from the

summer, 29% (n=7) from the fall, and 17% (n=4) from the winter (Figure 5).

This pattern is different in several ways from that at the Rosenstock site. First,

the mandibles indicate that a lower proportion of deer are being hunted in the

winter and spring. Second, the mandibles also indicate that a higher proportion

of deer are being hunted in the summer and fall. Third, the 15 cranially intact

antler, unlike the mandible distribution, indicate fall/winter hunting leaving only

the spring with a clearly lower rate of deer hunting.

Four of the species recovered at the Rosenstock are migrating birds

present in the area only in the winter. These species include the Common

Loon, the Whistling Swan, geese, and mergansers. These birds represent only

17% of the MNI for birds from this site. The remaining 83% of the birds

identifiable for MNI are present in the site vicinity year-round. This indicates

that, although the occupants of the site took advantage of the seasonal birds

that came into the area, they did not hunt only those birds. Instead, they

hunted a variety of species that were present throughout the year, whether

seasonally or not, taking advantage of the full range of resources available.

Wild turkey form the largest proportion of the birds recovered at the

Rosenstock site (NISP=394, MNI=23). Although available year-round, turkey

congregate into flocks in late fall and larger droves of two or more flocks in the

winter that last until late March, just prior to the breeding season. The

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beginning of the breeding season is also the time of year when males are at

their peak body weight (Smith 1975:77). Given these two factors, grouping and

increased body weight, fall and winter appear to be the most ideal times for

hunting large numbers of turkey with smaller amounts being hunted throughout

the rest of the year.

Neither the Winslow site nor the Shepard site assemblages contain

species of birds or fish that are available only on a seasonal basis. Both

assemblages do contain turkey, but, as stated above turkey are not a definite

seasonal indicator.

The fish in the assemblage at the Rosenstock site include both

catadromous and anadromous species. The catadromous species present at

this site is the American Eel. The American eel typically lives in streams with

permanent flow and then migrates to the Atlantic where they spawn and die.

These eels live for several years in one area before migrating to the sea so

they would have been available on a year-round basis at the site. There is one

anadromous species present in the Rosenstock sample, the Striped Bass. The

Striped Bass is considered a marine fish and ascends large river far upstream

to spawn. Spawning is typically done in the spring and it is then that this

species would have been available in the site vicinity.

Animal Selection

While animal diversity and seasonality of acquisition are important factors

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in describing the hunting patterns from these sites, other factors to be taken into

account include the selection of certain categories of individuals from various

species and how different animals were processed both in the field and in the

village. Hunting strategies include not only the decisions made about what

animals to hunt and when but also what is done with those animals after they

are killed. Processing in the field, or the removal or disarticulation of certain

elements in the field, will be discussed only for deer and will be done through

examining the distribution of skeletal elements. Processing at the site will be

examined using two types of data - fragmentation of specimens and the number

of various types of butchering scars. Deer is the only species with a sample

large enough and with elements complete enough to attempt this type of

examination.

When the ages from all 43 of the deer mandibles from the Rosenstock

site are examined, a hunting pattern utilizing all age classes can be observed.

One question that can be asked then is whether this sample indicates that

individuals were randomly killed or whether particular ages of deer were

preferred over others. Munson (1991), extrapolating from data compiled by

Emerson (1980) constructed a distribution of the proportions of deer dying in a

natural population for a series of six age classes. The distribution of ageable

mandibles from the Rosenstock site differs slightly from this natural distribution

(Figure 6). The first three age classes (less than one year, one-to-two years,

and two-to-three years) are slightly underrepresented in the Rosenstock

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 222 Population Population Natural Population* Population* Natural “ Rosenstock “ 4 "

Figure 6 Age 2-3 3-4 4-5 5+ The Rosenstock Site 1-2 *From Emerson (1980) extrapolated by Munson (1991) Age Composition of Deer Populations <1 15 10 25 40 35 20 30 Q_

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sample. The next two age groups, however (three-to-four years, and four-to-

five years), are overrepresented with the final age group (over five years) being

very similar to the natural population. The occupants of the Rosenstock site,

then, were hunting fewer younger individuals and more older individuals than

would be expected in a normal population die-off pattern. One reason for this

selection could be that individuals in the three-to-four year and four-to-five year

age groups have achieved their maximum body weight and therefore result in

more meat for each kill. This pattern then indicates that hunting was not purely

random but was selective - selective for older and larger individuals. This

agrees with the conclusions reached by the examination of the antler: that older

and larger individuals were being hunted. In addition, these larger individuals

were probably being hunted more heavily in the fall when their body weight was

at its annual maximum.

The hunting pattern illustrated by mandibular ages at the Winslow site is

very different from that at the Rosenstock site and from the die-off pattern of a

normal population (Figure 7). A total of 59 ageable mandibles are in the

sample from the Winslow site. The distribution of animals within the six age

classes is u-shaped with higher proportions (25% each) of individuals being

hunted at the youngest and oldest age classes with the remaining individuals

distributed more evenly throughout the middle four age classes. If this sample

is representative of the hunting pattern used by the occupants of the site then it

appears that they are hunting the age classes easiest to hunt - the younger and

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*c S30 c m o 3 '.S3 OCL JS CL 3 5 a. o o ID CL C <0 z t *

lueojdd

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the older individuals least able to flee. This pattern could result from many

factors, not only a choice preference for young or old individuals. This could

also indicate that not as much time was devoted to hunting, waiting for the

optimum sized individual, but instead taking the first deer that they could kill,

the ones least able to get away.

No ageable mandibles were identified in the sample from the Shepard

site.

Mandibular tooth eruption and wear can also be used to determine age

within certain classes for raccoon. In addition, sexual dimorphism in the root

size of canines can be used to determine the sex of the individual raccoon. Of

the MNI of 10 for raccoon from the Rosenstock site, nine are represented by

ageable mandibles (Table 17). Grau et al. (1970) define five age classes for

categorizing tooth eruption and wear patterns. At the Rosenstock site seven of

these (78%) were in the older two age classes with one each in the second and

third age classes and none in the youngest age class. While this does not

represent a normal population distribution, this could very well be due to sample

size. In a population of any animal, you would expect to find the most

individuals at the youngest age classes and then decreasing amounts at

subsequent classes until all of the population dies. The ages of the dead

individuals should then reflect this pattern. The pattern at the Rosenstock is

instead the reverse of this with fewer individuals in the younger age classes

and more individuals in the older age classes. Four of the raccoon mandibles

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had canines intact and could therefore be sexed. Two of the individuals were

male and two were female. Because of the small sample size no conclusions

can be drawn from these data except to say that both sexes were being hunted

and there was no deliberate and total exclusion of hunting one sex of raccoon.

Twenty-eight ageable raccoon mandibles were recovered from the

Winslow site. These were distributed in all five age classes with 14% (n=4) in

age class one, 14% (n=4) in age class two, 29% (n=8) in age class three, 11%

(n=3) in age class four, and 32% (n=9) in age class five (Table 17). At the

Shepard site, 18 ageable mandibles were recovered and included 22% (n=4) in

age class one, 28% (n=5) in age class two, 28% (n=5) in age class three, 5%

(n=1) in age class four, and 17% in age class five. Eleven raccoon mandibles

with few or no teeth present were also in the Shepard site assemblage. Neither

of these assemblages indicates a clear preference for individuals from certain

age classes but instead are distributed, albeit relatively unevenly, throughout all

five age classes.

Animal Processing

The distribution of deer skeletal elements (as measured with MNE)

varies greatly from element to element at the Rosenstock site (Table 16). If

complete skeletons were being brought from the hunting site to the village for

processing, then the distribution of these elements throughout the body should

match closely to the distribution of these elements in a standard deer with all

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TABLE 17

RACCOON MNI BY SITE AND AGE CLASS

SITE AGE LEFTRIGHTPAIRS MNI CLASS

18FR18 2 1 N/A 1

18FR18 3 1 N/A 1

18FR18 4 3 N/A 3

18FR18 5 1 3 NONE 4 TOTAL 9

18M01 1 1 N/A 1 TOTAL 1

18M09 1 2 2 NONE 4

18M09 2 2 2 NONE 4

18M09 3 4 4 NONE 8 18M09 4 2 1 NONE 3

18M09 5 3 6 NONE 9 TOTAL 28

18M03 1 4 N/A 4

18M03 2 2 3 NONE 5

18M03 3 5 N/A 5

18M03 4 1 1 1 1

18M03 5 4 1 NONE 3

18M03 ? 9 3 1 11 TOTAL 29

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elements intact. To examine this, elements were divided into four categories -

forelimb, hindlimb, unspecified lower limb, and axial elements. Forelimbs

include from the scapula and humerus to the carpals, hindlimbs include from

the pelvis to the tarsals, unspecified lower limb elements include the sesamoids

and phalanges, and axial elements include the skull (including mandible) and

vertebra. The proportions of elements in each of these categories were then

calculated for each site and for a standard deer skeleton.

As can be seen in Figure 8, there are some clear differences between

the proportions of elements at the Rosenstock site and those of the standard

deer. All limb bones are slightly overrepresented with hindlimbs showing the

greatest degree of elevation. Axial bones are grossly underrepresented with

only approximately one half the proportions in the Rosenstock sample as are in

the standard deer. When examined more closely we can see that for the atlas

and axis, the MNEs are 20 and 24 respectively. The MNI for deer overall

however is 69, much higher than is indicated by the MNEs for axial remains.

When compared to the number of axial remains that would be expected given

the MNI, the axial remains are even more underrepresented with less than a

third of the expected MNE for 69 individuals.

Some of this distribution could be attributed to differential taphonomic

processes, with the sturdier limb bones having more fragments preserved and

identifiable to element than the more fragile vertebrae. However, it is more

likely that this distribution is the result of differential prehistoric retention of

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H Rosenstock BStandard Deer

Figure 8 Body Part The Rosenstock Site ------— Percentages of Deer MNE by Body Part ------80 100 r —

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skeletal elements at the village. Although vertebrae are frequently highly

fragmented, many of these fragments are still relatively identifiable. While the

precise vertebra location cannot be identified, the type of vertebra (i.e., cervical,

thoracic, etc.) could be identified, and this level of identification was considered

sufficient for inclusion of a fragment in the MNE calculations. As a result, while

the vertebrae may be slightly underrepresented because of their fragmentation,

I do not feel that this potential underrepresentation is severe enough to warrant

negating the obvious low frequency of axial remains in this assemblage.

The unspecified limb elements, consisting of lower limb elements

unassignable to forelimb or hindlimb (phalanges and sesamoids) are slightly

higher proportionally in the Rosenstock assemblage than those from a standard

deer. When the MNE for those elements are compared to what would be

expected with an MNI of 69, however, these elements are extremely low. With

phalanges, for example, an MNI of 69 would yield 552 of each bone. In the

Rosenstock assemblage however, there are only 126 first phalanges, 91

second phalanges, and 49 third phalanges. The lower limb bones identifiable

to forelimb or hindlimb are also underrepresented with very low numbers for

metacarpals, metatarsals, and all other carpals and tarsals.

The combination of these two patterns, proportionally fewer lower limb

bones and axial bones, indicates that there was probably some initial cleaning

of the skeleton at the hunting site that resulted in the lower limb bones and

much of the axial skeleton being removed before the remaining meat was

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brought back to the village. Although metacarpals and metatarsals are

frequently used as tools, the other carpals, tarsals, and phalanges are rarely

used as tools and also yield virtually no meat and little marrow. Their utility

therefore is very limited, and there would be little incentive for bringing these

parts back to the village. Although more meat is found associated with the

vertebra than with the lower limbs, much of that (such as the tenderloin) can be

quickly removed leaving the vertebrae behind. Vertebrae are also rarely used

for tools although they can yield high amounts of marrow depending on how

they are cleaned and disarticulated. It is the upper limb bones that are highest

in meat yield, that yield high amounts of marrow, and that are most frequently

used for tools. It is not surprising, therefore, that these are the most frequently

recovered elements at the site.

The Winslow site has a limited number of elements represented for deer

(Table 16). For both hindlimbs and forelimbs, it is primarily the upper limb

bones that are present in the assemblage. The MNI for deer for this site is 44

and is based on mandibles. None of the limb bones come close to the counts

for what would be expected for 44 individuals. As can be seen in Table 16,

one metacarpal and one carpal were in the sample. Tarsals are slightly better

represented with 17 metatarsal specimens and 27 tarsals. When the elements

are divided into the four categories of general body part, the forelimbs are

exactly the same proportion as for the standard deer, the hindlimbs are almost

twice as high as expected for the standard deer, the unspecified lower limb

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bones are a little over half of what is expected for the standard deer and the

axial bones are only slightly lower than expected for the standard deer (Figure

9). The hindlimb and the unspecified lower limb categories are most different

from the standard proportions. As with the material from the Rosenstock site, it

is possible that the lower limb bones were removed in the field prior to the

hunters' returning to the village. Given the sample size for this assemblage,

however, some of this uneven distribution could also be due to collection

strategy.

Although the proportions of axial bones as a general category are fairly

close to that expected for a standard deer, the distribution of elements within

that category is very uneven. Mandibles and maxillae are well represented, but

the remaining elements in the category are underrepresented. Indeed,

mandibles are the highest represented element and is the element used to

calculate the MNI. Given the large numbers of mandibles compared to other

elements for this sample, and given that all of them are complete enough to be

aged, there appears to have been a bias in the collection strategy for this

element.

The distribution of deer skeletal elements by general body part from the

Shepard site is the most unlike the standard deer of the other Montgomery

Complex sites (Figure 10). While the forelimbs are slightly elevated in

proportion, the hindlimbs are almost three times the expected proportion, the

unspecified lower limb bones are two and one-half times the expected

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

Percentages of Deer MNE by Body Part O D CM o o CD o o CO o O o e6eju0oj0d 233

Figure 9 Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

Percentages of Deer MNE by Body Part

The Shepard Site o o o o o o o o O CM f T 0 ( GO O eeeiueojad 234 Q O 0)

Figure 10 235

proportion, and the axial elements are only one-fifth of the expected proportion

for the standard deer. In addition, the MNI for deer for this assemblage is only

four. Only five of the 18 elements represented have an MNE greater than one.

As discussed in Chapter Three, the collection strategy at this site limits the

interpretations about subsistence patterns that can be made from this sample.

While broad interpretations about the general distribution of animals or the

presence of certain species can be discussed, more detailed observations such

as those performed by examining closely calculated figures such as MNE or

MNI cannot be made. Interpretations about the implication of missing elements

or absent species of animals could be totally misleading due to biases in

collection strategy.

Butchering Patterns

Butchering scars were examined only for the assemblages from the

Rosenstock and Hughes sites. The material from the other sites are biased in

various ways and the distribution of the various butchering scars was not felt to

be representative of butchering activities at these sites. A total of 276

butchering scars were examined from the Rosenstock site (Table 18) (see

Appendix 4 for a listing of data on all of these scars). Using categories defined

by Binford (1981), dismembering scars are 46% of the sample, filleting scars

are 31%, breaking scars (usually spiral fractures or heavy blows done to break

long bone shafts) are 20%, and skinning scars are three percent (Table 19). In

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TABLE 18

DISTRIBUTION OF NUMBER OF BUTCHERING SCARS FOR ROSENSTOCK (18FR18) AND HUGHES (18M01)

SCAR TYPE

M F FL D B S K

Rosenstock Fea. 2 2 Fea. 4 3 3 ---- - Fea. 5 39 19 -- 21 4 - Fea. 6 2 -- - 1 -- Fea. 10 - -- - 1 -- Fea. 12 59 28 1 1 23 2 1 Fea. 17 4 8 -- 2 -- Fea. 27 4 1 - - -- - Fea. 35 1 ------

Non-Fea. 11 25 -- 8 2 -

Total 125 84 1 1 56 8 1

Hughes Fea. 22 10 5 1 . 6 Fea. 45 4 1 - - 1 1 -

Non-Fea. 5 10 - - - - -

Total 19 16 1 - 7 1 -

Key to Abbreviations: M = Dismembering F = Filleting FL = Flaking D = Defleshing B = Breaking S = Skinning K = Killing/Food Preparation

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TABLE 19

DISTRIBUTION OF PERCENTAGES OF BUTCHERING SCARS FOR ROSENSTOCK (18FR18) AND HUGHES (18M01)

SCAR TYPE

M F FL D B S K

Rosenstock Fea. 2 100 Fea. 4 50 50 -----

Fea. 5 45 23 - - 25 5 -

Fea. 6 67 -- - 33 --

Fea. 10 -- - - 100 -- Fea. 12 51 24 1 1 20 2 1

Fea. 17 29 57 - - 14 --

Fea. 27 80 20 --- - - Fea. 35 100 ------

Non-Fea. 24 55 -- 17 4 -

Total 46 31 20 3

Hughes Fea. 22 45 23 5 . 27 Fea. 45 58 14 -- 14 14 -

Non-Fea. 33 67 -----

Total 44 36 2 - 16 2 -

Key to Abbreviations: M = Dismembering F = Filleting FL = Flaking D = Defleshing B = Breaking S = Skinning K = Killing/Food Preparation

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addition, one each of flake scars, defleshing scars, and killing scars were

identified. Given this distribution, the major activities that these data indicate

are dismembering the carcass, filleting the meat from the bones, and then

breaking the bones, probably for marrow extraction. Little evidence of skinning

or broader defleshing (as opposed to the finer filleting) occurs. The lack of

skinning scars may be accounted for by the low numbers of lower limb

elements in the assemblage rather than by concluding that skinning was not an

activity performed on these animals. Skins are frequently cut from the body

down to the lower limbs where those parts are removed and, at this site, left in

the field and not brought back to the village. While skinning was probably

occurring, the techniques involved cannot be addressed since these data are

not present. Instead, what can be concluded is that skinning activities occurred

away from the site, while other meat removal and marrow extraction activities

were performed within the village.

Animal Utilization at Lurav Focus Sites

Diversity

The assemblage from the Hughes site is the only primary assemblage

for this complex. It contains a limited variety of animals, with amphibians

present but none identifiable to family or better, three identifiable species of

turtles, three identifiable species of birds, one identifiable species of fishes, and

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fifteen identifiable species of mammals (Table 12). As with the material from

the Rosenstock site, the MNI for many of these species is low (Table 14).

Flotation material was not available for this analysis, and all distributions and

conclusions here are based only on material screened through 1/4 inch mesh.

The impact of the inclusion of the flotation material would probably be on those

classes of animals that leave very small remains - fishes, birds, amphibians,

and reptiles. Because of this it is probable that these classes of animals are

underrepresented in the current assemblage. All of these classes of animals

are present in the analyzed screened assemblage, so some sample of them

has been analyzed, but predicting the degree of their underrepresentation is not

possible.

Material identifiable to class at the Hughes site are distributed much less

evenly than those at the Rosenstock site. Mammals constitute 91% of the

NISP by class in this assemblage. Reptiles, predominantly turtles, and birds

each represent five percent of the NISP by class. Fish and amphibians each

represent less than one percent of the NISP by class.

Deer are the most frequently identified species in this assemblage. Deer

account for 69% of the NISP identifiable to a level of family or better for all

classes, and 93% of the mammals identifiable to a level of family or better.

Turtles are the next most frequent remains with 23% of remains identifiable to

the level of family or better. As with the Rosenstock assemblage, this figure for

turtle NISP could be misleadingly high, since most of the identifiable turtle

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remains were either carapace or plastron fragments. The MNI figure for turtle,

which was calculated using bone fragments rather than carapace and plastron

fragments is only three, a figure that is probably a more accurate representation

than the NISP is of the importance of turtle in the diet of the inhabitants of the

site.

Gray squirrel represent one percent of the NISP identifiable to the level

of family or better for all classes of animals in the Hughes site assemblage.

Although turkey (n=41) and raccoon are the next most frequently recovered

species, they each represent less than one percent of the NISP for all animals

identifiable to the level of family or better. All other identified species also each

represent less than one percent of the NISP. Meat weights will not be

calculated for the Hughes site assemblage because of the consistently low MNI

figures. Given these low figures, with few exceptions, calculating the meat

weights would not change the ranking of species in order of dietary importance

much differently than what they are using NISP or MNI.

The Hughes site is located approximately 300 feet north of the north

bank of the Potomac River in a floodplain environment. All of the species

recovered in the Hughes site assemblage can be found in the immediate site

vicinity at some point of the year. Most of these are available year-round. One

exception is a migrating bird, the Whistling Swan, Olor columbianus. The

Whistling Swan is found in the site vicinity only in the winter. As discussed

above, elk are typically up in mountains in the spring and summer and down in

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valley areas in the fall and winter. It is possible that the inhabitants travelled

into more mountainous areas to hunt elk in the spring and summer. It is more

likely however that elk were hunted when they moved into their winter grounds

in the valley areas that would have been closer to the site. Early in these

seasons is also the time when elk would be at their peak body weight and

would be optimal for hunting. The implications of the presence of these species

will be discussed below.

In sum, the Hughes site environs include a number of habitats and could

have provided a wide variety of animals, both terrestrial and aquatic, for

subsistence purposes to the inhabitants of the site. It does not appear,

however, that the occupants of the Hughes site fully utilized all of these

habitats. Instead, the pattern as evidenced by this sample, indicates that

hunting focussed on a few terrestrial species, mainly deer, squirrel, turkey and

raccoon, with the hunting and fishing of other species incidental in their

contribution to the diet. The more prevalent species can regularly be found in

forest edges or in shrubby areas that would be found adjacent to agricultural

fields. Deer today are frequently found browsing in these edge habitats and in

fields, and it is likely that they would have done the same prehistorically.

The assemblage from the Keyser Farm site, as discussed in more detail

in Chapter Three, cannot be considered representative of the subsistence

activities occurring at this site. The Keyser Farm assemblage contains no

amphibians or fish and only one reptile (turtle) are present in the sample

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available for this study. One species of bird was identified and four species of

mammals. The mammal remains comprise 59% of the material identifiable to

class with the bird remains at 11 % and reptiles at 30%. With no screening

most of the smaller fragments and therefore the smaller taxa were not

recovered. The diversity of taxa at the Keyser Farm sites is extremely low

when compared to any other site in this study. It is not possible to determine to

what extent this is due to a lower diversity of taxa being used by the inhabitants

of the site or due to collection methods. As we can see above, the primary

assemblage from the Luray Focus, the Hughes site, appears to be less diverse

than that of the primary assemblage from the Montgomery Complex, the

Rosenstock site (a more detailed comparison and testing of this observation

can be found below). If this pattern continues, then we would expect to find a

relatively low diversity of taxa in the Keyser Farm site. Still, it is not possible to

determine if the low diversity observed in this assemblage is the result of

collection strategy or is an actual assemblage characteristic. It is interesting

and perhaps significant though that the curated early assemblages from the

Montgomery Complex are relatively higher in diversity while the assemblage

from the Keyser Farm site is relatively low in diversity.

Not surprisingly, deer were the most frequently identified animal in this

assemblage (NISP=138). They are 56% of the specimens from all classes

identifiable to the taxonomic level of family or better and 98% of the mammals

identifiable to the family or better (Table 13). Turtle (NISP=99) are the next

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most frequently identified animal and are 100% of the reptiles recovered and

40% of all animals identified to at least the level of family. As with the other

secondary assemblages discussed above, the turtle remains collected consisted

primarily of carapace and plastron. Because of this, the relative importance of

turtle in the diet of the occupants of this site is very possibly overrepresented in

this assemblage. Turtle carapaces were frequently altered to be used as tools,

especially as cups or bowls. The excavators at this site were aware of this,

and the high frequency of turtle carapace may very well be the result of this

knowledge and the intent of the excavators to collect deliberately modified or

utilized bone.

Ten turkey bones were identified and they represent 100% of the

identifiable birds and four percent of remains from all classes that were

identifiable to at least the level of family. The only other identifiable animals in

this assemblage are fox (NISP=1), raccoon (NISP=1), and elk (NISP=1). All

other remains in the assemblage were identifiable only to class.

A total of 374 specimens were identifiable to class in the assemblage

from the Shepard Barrack site. Of these 90% are mammal, seven percent are

bird, three percent are reptile, and less than one percent are fish.

Approximately less than half of the remains identifiable to class were identifiable

to family. However, the distribution of these is very similar to that at the class

level. Of the remains identifiable to family 89% are mammal, seven percent are

reptile, three percent are bird, and one percent are fish.

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As at most of the sites in this study, deer are the most ubiquitous

species in the assemblage (NISP=150). They are 84% of the remains

identifiable to family, 94% of the mammal remains identifiable to family, and

40% of all remains identifiable to class (Table 13). The only other mammal

identified in the sample with an NISP greater than one is elk (NISP=3). Other

mammalian species identified include the eastern cottontail, woodchuck,

beaver, fox, and raccoon. Turtle (NISP=12) are the only species of reptile

identified and turkey (NISP=6) are the only species of bird identified. The only

fish specimen in the assemblage was one fragment of sturgeon. This specimen

was not identifiable to species.

All of the remains could have been found in the immediate vicinity of the

Shepard Barrack site. Since sturgeon is an anadromous fish, it would have

been available on a seasonal basis. The largest of the bony fishes, sturgeon

can weigh over 2500 pounds (Robins et a/. 1986:46). Given this size range,

regular acquisition of this fish could have represented a significant part of the

diet of the occupants of this site.

Seasonality

Seasonal indicators at the Hughes site are few. Three intact antlers

were recovered, but no crania with evidence of shed antler were in the

assemblage. In addition, only three mandibles complete enough to be aged

and young enough to indicate season of kill are present. Of these three

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 245

mandibles, two are from the spring and one from the fall (Figure 5). While

these mandibles indicate that deer were definitely hunted in the spring and fall,

the sample is not large enough to conclude that deer were not hunted at other

times of the year. No intact antlers or young, complete mandibles were present

in either the Keyser Farm or the Shepard Barrack samples.

One species of migrating bird, the Whistling Swan (MNI=3, NISP=15), is

present in the Hughes site assemblage. Turkey (MNI=7, NISP=41) is the most

frequently identified bird from this site. Only one other species of bird, the red­

tailed hawk, was recovered from the Hughes site. Given the fact that this

assemblage was recovered with good control and collection strategies, it is

surprising that more bird remains are not present in this assemblage. If,

because of the detailed collection strategy, we can assume that the

assemblage is representative of the remains at the site, then it is significant that

such a high proportion of the few birds that are present in the sample are from

this seasonal species (swan). This would indicate that although some species

could have been hunted throughout the year, bird hunting at the Hughes site

was done mainly in the fall. No migrating birds are present in either the Keyser

Farm or the Shepard Barrack samples. Few fish were recovered at any of the

Luray Focus sites and none of the fish recovered can be used as seasonal

indicators.

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 246

Animal Selection

Eleven ageable deer mandibles were identified in the assemblage from

the Hughes site. Of these, one (9%) is less than one year old, one (9%) is in

the one-to-two year old group, two (18%) are in the two-to-three year old group,

two (18%) are in the three-to-four year old group, four (37%) are in the four-to-

five year old group, and one (9%) is in the five year and over age group (Figure

11). In this distribution only one age class, the oldest, matches the natural

population distribution. For the other age classes, the Hughes site distribution

is almost the opposite of that of the natural population with fewer individuals in

the younger age classes and more individuals in the three middle adult age

classes. This could indicate selective hunting for older and larger individuals.

This pattern could also be a result of the small number of mandibles in the

sample. The assemblage as a whole, however, is considered representative of

the subsistence activities at the site, so there is no reason to suspect that this

particular element would not be representative. If this is so, then an argument

could be made for selective deer hunting at the Hughes site, with selectivity

being for older individuals.

Only two ageable mandibles were identified in the sample from the

Shepard Barrack site. One of these was in the two-to-three year old age group

and one was in the five year and over age group. Given the small sample size

no conclusions can be drawn from these two specimens. No ageable

mandibles were identified in the Keyser Farm assemblage.

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Population Natural Population* H ughes

5 + 3-4 4-5 Figure 11 Age The Hughes Site 2-3 1-2 *From Emerson (1980) extrapolated by Munson (1991) Age Composition of Deer Populations <1 IO 40 30 20 CL­

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. One ageable raccoon mandible was recovered at the Hughes site. It is a

male in age class one. No ageable raccoon mandibles were recovered from

either the Shepard Barrack site or the Keyser Farm site. Given this, no

conclusions can be drawn about raccoon hunting at any of these sites or for the

Keyser Focus in general.

Animal Processing

The distribution of the proportions of skeletal elements for deer by body

part can be seen at the Hughes site in Figure 12. When compared to the

distribution of elements in a standard deer skeleton there are some key

dissimilarities that need to be addressed. The first of these is that numbers of

both the forelimb and the hindlimb elements are approximately 10% higher in

the archaeological assemblage than in a standard deer skeleton. The MNI for

deer at the Hughes site is 19. Many of the MNEs for upper limb elements are

in this range while many of the lower limb elements are not. It is the high meat

bearing elements which are best represented - the scapulae, humeri, tibiae, and

femura. In addition, the metacarpals and metatarsals are well represented.

These elements were frequently used as tools, however, and their curation

prehistorically in the assemblage could be a function of this use rather than of

their relative dietary importance.

The unspecified lower limb elements (metapodials and phalanges) are

slightly overrepresented proportionally in the assemblage at 18%. The standard

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

Percentages of Deer MNE by Body Part CO JC 1“ 1 -C +-» O) 0

eBe^uQOjed 249 CO ■o CL d (0 O > LJL T— CM CD 0 IS u_ 250

deer skeleton is only 11% metapodials and phalanges. However, when the

MNEs for these lower limb elements are compared to what would be expected

for 19 individuals, these elements all appear to be very low. Finally, axial

elements are only slightly more than one-half of what is expected in a standard

deer. In particular, atlas with an MNE of four and axis with an MNE of two are

very low. The remaining vertebra and other axial elements are all also equally

low except for the pelvis. Thirty-eight pelvic elements were identified, a

representation equal to many of the upper limb elements. Unlike the other axial

elements however, the pelvis is part of a high meat yielding area of the body so

it is not surprising that its representation is similar to that of the other high meat

yielding areas.

Deer skeletal elements represented at the Keyser Farm site are very

limited. One radius, one ulna, and one tibia are the only high-meat bearing

elements represented. Most of the elements in this assemblage are

metacarpals and metatarsals (Table 16) and most of them are worked. Indeed,

metapodials account for 46 of the 50 identifiable elements in the assemblage.

This unevenness of the distribution of proportions of body parts contrasts

sharply with that of the standard deer skeleton (Figure 13). This distribution of

elements and the distribution of their proportions by body part supports the

conclusions that were reached in Chapter Three - that due to collection biases

this assemblage is not accurately representative of the dietary remains at the

site. As a result no conclusions can be reached regarding possible processing

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t 0 QL > ■o O

n § in £ z 0 L i. i_ ■c 0 0 0 Q_ > > ■D Figure 13 O CQ 0 ® 0 -C O) H 0 ■H c 0 O 3>_ 0 CL

0BBlU0OJ0d

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tasks performed away from or at the village itself.

The Shepard Barrack site deer assemblage has a higher representation

of elements than that from the Keyser Farm site. Except for carpals and

tarsals, most of the skeletal elements are represented. The distribution of these

elements by body part is not unlike that seen in other assemblages with

overrepresentation in the forelimb and hindlimb elements and

underrepresentation in the axial elements (Figure 14). The MNI for deer at the

Shepard Barrack site is seven. Again, it is some of the high meat yielding

elements that are closest to meeting this figure, with 12 humeri, seven radii, five

femura, six tibiae, and 13 pelves identified. No atlas or axis and only five other

vertebrae were present in the assemblage. Given the conclusions reached in

Chapter Three, that this assemblage appears to be somewhat representative of

the dietary remains at this site, this assemblage can be used to support the

conclusions reached with the data from the primary assemblages. The element

and body part distribution patterns described for this assemblage indicate that,

as at some of the other sites, there appears to have been a preliminary

processing of deer carcasses in the field prior to their return to the village site.

Butchering Patterns

Data on animal processing as evidenced by the distribution of butchering

scars for the Luray Focus are limited to those at the Hughes site. A total of 44

butchering scars were observed on the faunal material in the Hughes site

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Standard Deer 0Shepard Barrack S S

Figure 14 Body Part The Shepard Barrack Site Percentages of Deer MNE by Body Part 100 CD O) C (D 03 CD O i— CL o CD Q. Q. C with permission of the copyright owner. Further reproduction prohibited without permission. 254

assemblage (Table 18). Dismembering scars comprise 44% of the scars

observed, filleting scars are 36%, breaking scars (usually of long bone shafts)

are 16%, and skinning scars and flaking are two percent of the butchering scar

sample (Table 19). The rank order of activities that these data indicate were

occurring at this site were: 1) the dismemberment of the carcass; 2) the

removal of the flesh; 3) and the breaking of long bones, probably for marrow

extraction. The low frequency of skinning scars indicates that skinning of the

animals was either occurring off-site or that the bones that would most likely

contain this evidence (the crania, upper vertebra, and lower limbs) were

deposited elsewhere. Because these are the same elements that are poorly

represented in the distribution of skeletal elements for deer, it is possible that

skinning the animal and removing the non-meat bearing elements was

occurring at the hunting camp prior to bringing the animal back to the village.

The meat processing and marrow extraction activities then, appear to have

been performed at the village.

Comparison of Animal Utilization Patterns at Montgomery Complex

and Lurav Focus Sites

The main features in animal utilization strategies to be compared

between these two archaeological complexes are the diversity of animals being

hunted, the emphasis of seasons in which various hunting activities were

performed, if criteria were used in selecting individual animals, and what

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processing activities were being performed away from the village at the hunting

site if indeed it appears that the hunting site was away from the village. The

remainder of this chapter will be used to define and compare these features for

the two complexes and to determine if differences between them are

statistically significant or due to various sampling strategies. The conclusions

that can be drawn from these differences and similarities and the implications of

these results will be discussed in depth in the following final chapter.

Diversity

The diversity of animals being hunted at the sites in the Montgomery

Complex and Luray Focus will be compared to determine if whole classes of

animals as well as certain species of animals are being hunted in different

proportions. Because of both the uneven distribution of specimens between

species and the low number of specimens for most of the species identified, all

of the statistical comparisons for these assemblages will be performed on the

taxonomic level of class by summing the MNIs or NISPs calculated within those

classes. Similarity and difference between the two primary assemblages will be

tested statistically using the Shannon-Weaver Index for evenness and richness,

and Chi-Square and Kolmogorov-Smirnov to determine if any observable

differences between the two assemblages illustrated by Shannon-Weaver are

significant. To provide basic statistical descriptions of this diversity, the

Shannon-Weaver index will be used and will be calculated using combined MNI

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figures summed by class. When comparing the diversity in the two primary

assemblages the basic comparative question is "Is one assemblage significantly

more diverse than the other?" Both Chi-Square and Kolmogorov-Smirnov will

be calculated using NISP figures combined by class to address this question.

When the calculations for evenness and richness are performed for the

primary assemblages (Table 20) two very different sets of figures result.

(These figures will be rounded to the nearest hundredth for this discussion.)

Evenness at the Hughes site is .33 and richness is .47. Evenness at the

Rosenstock site is .52 and richness is .74. The two figures taken together

indicate overall diversity of an assemblage. This difference in these figures

indicates that not only were more types of animals being hunted at the

Rosenstock site (indicated by the higher richness value), but that the animals

that are being hunted are more evenly distributed across all of the classes

(indicated by the higher evenness figure). I can conclude from this observation

then that the occupants of the Rosenstock site were hunting a more

consistently diverse distribution of animals by class.

Given the conclusion that the Rosenstock assemblage is more diverse

than the Hughes site assemblage, the next issue to be addressed is whether or

not that difference is significant at a given level. If the assemblages are

significantly different then reasons for this difference must be postulated. For

both significance tests performed below, the null hypothesis is that there is no

significant difference in the distribution of specimens (NISP) among taxonomic

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TABLE 20

SHANNON-WEAVER INDEX CALCULATIONS COMPARING EVENNESS AND RICHNESS FOR THE ROSENSTOCK AND HUGHES SITES

Hughes Site

Class MNI % log0% | loge%(%) |

Amphibian 0 0 0 0 Reptile 3 0.050847 -1.29373 0.06578 Bird 11 0.186441 -0.72946 0.13600 Fish 1 0.016949 -1.77085 0.03001 Mammal 44 0.745763 -0.12740 0.09501

Evenness 0.326810 Richness 0.467556

Rosenstock Site

Class MNI % loge% | loge %(%) |

Amphibian 9 0.039823 -1.39987 0.05575 Reptile 11 0.048673 -1.31272 0.06389 Bird 38 0.168142 -0.77432 0.13020 Fish 39 0.172566 -0.76304 0.13168 Mammal 129 0.570796 -0.24352 0.13900

Evenness 0.520510 Richness 0.744684

classes between the Rosenstock and Hughes sites. If null hypothesis is

disproved, then it is possible that there is a significant difference in the

distribution of specimens (NISP) among the taxonomic classes between the

Rosenstock and Hughes sites.

The Kolmogorov-Smirnov test consists of two steps - calculating the

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greatest difference of cumulative frequency by class and then comparing this to

the calculated minimum expected value for the desired confidence level. Table

21 shows that the greatest observed difference of cumulative frequency is .085.

Minimum expected values were calculated for three confidence levels, .05, .01,

and .001. Given that the observed greatest difference of cumulative frequency

is greater than the minimum expected values for any of the calculated

confidence levels, the null hypothesis can be rejected. In summary, then, the

Kolmogorov-Smirnov test indicates that it is possible that the distribution of

specimens among classes between the Rosenstock and Hughes sites is

significantly different.

TABLE 21

KOLMOGOROV-SMIRNOV TEST CALCULATIONS FOR THE DISTRIBUTION OF SPECIMENS (NISP) BY CLASS FOR THE ROSENSTOCK AND HUGHES SITES

Rosenstock Hughes

Class % Cumulative % Cumulative Difference % %

Amphibian .003 .003 .000 .000 .003 Reptile .069 .072 .046 .046 .026 Bird .071 .143 .045 .091 .051 Fish .035 .178 .002 .093 .085 Mammal .822 1.000 .907 1.000 .000

Observed Greatest Difference of Cumulative Frequency.085 Minimum value required at significance of .05 .011 Minimum value required at significance of .01 .013 Minimum value required at significance of .001 .002

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The final test used to determine significance of similarity between two

assemblages is chi-square. As discussed above, chi-square does not measure

the strength of a relationship, only if a relationship exists. Because the results

of the chi-square test can be influenced by the size of the sample(s), once the

minimum value for significance at a given level is reached the results are

considered significant. Whether the calculated value is only slightly higher or

extremely higher than the required value does not increase the significance or

indicate a stronger relationship. The chi-square value in Table 22 was

calculated using dBASE Stats. This software package calculates the value and

indicates the significance level at which the value was reached. Significance

levels can be calculated for up to five places to the right of the decimal point -

much higher levels than those that were calculated for Kolmogorov-Smirnov - if

the results are indeed significant at that high a level. The chi-square value for

these assemblages is 1131.41223, and is significant at a level less than .00005.

Since many significance tests are calculated at levels of .05 or .01 and the .001

level is considered to be rigorous enough for most relationships, this

significance level is more than sufficient to test the hypothesis. Given that the

acceptance of the null hypothesis would indicate that there is no significant

difference in the distribution of specimens among the taxonomic classes

between the Rosenstock and Hughes sites, with the significance level of .00005

achieved, we can conclude that the null hypothesis can be rejected and that the

difference in taxonomic distribution between Rosenstock and Hughes is significant.

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TABLE 22

CHI-SQUARE CALCULATIONS FOR DISTRIBUTION OF SPECIMENS BY CLASS FOR THE ROSENSTOCK AND HUGHES SITES

Class Amphibian Bird Fish Mammal Reptile Total

Hughes 2 980 46 19570 993 21591 (30.2%)

Rosenstock 146 3560 1764 40932 3424 49826 (69.8%)

Total 148 4540 1810 60502 4417 71417 Total % .2 6.4 2.5 84.7 6.2 100.0

Chi-Sauare Degrees of Freedom Significance 1131.41223 4 <.00005

With the observations described earlier in this chapter for each complex

and the statistical results described above, I argue that there are some very

basic differences between the primary assemblages in relation to assemblage

diversity. First, the occupants of the Rosenstock site are hunting many more

species of animals than are the inhabitants of the Hughes site. Second, not

only are more species of animals being hunted at the Rosenstock site, but

these species are distributed throughout the various classes of animals. Third,

the breadth of hunting at the Rosenstock site is fairly consistent throughout the

classes. Hunting a variety of species in each class is not a deviation from the

regular hunting patterns but is rather an integral part of the regular hunting

pattern. In addition, this pattern is significantly different than that found at the

Hughes site. Although the samples from the secondary sites are not

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representative enough to be statistically tested against this model, there are

some indications with the number of taxa from a variety of classes at Winslow

and Shepard that this pattern carries through for the other sites from these

complexes.

Seasonality

Seasonality indicators from Montgomery Complex sites indicate that deer

were being hunted throughout the year and that other seasonal resources were

hunted as they became available. At the Rosenstock site, the mandibular data

indicate that more deer were being hunted in the spring. The intact antler

figures however, indicate that a considerable number of the deer in this

assemblage were hunted in the winter. These data are not contradictory,

instead they seem to indicate that deer were being hunted relatively

consistently throughout the year. The mandibular data are representing those

individuals hunted in the spring while the antler data are representing those

individuals hunted throughout the rest of the year. When the age distribution of

deer is added, it is obvious that older deer at their prime meat-bearing size

were being hunted most frequently. One possible conclusion that could be

drawn from these data is that older (and larger) individuals were hunted more in

the fall or winter (evidenced by the intact antler) when they are at their yearly

peak weight.

The seasonal indicators for deer from the Winslow site yield similar

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results. The mandibular data indicate year-round hunting with an emphasis in

the spring and fall, but the high number of intact antlers indicate that more deer

in the assemblage were indeed hunted in the fall or winter than the mandibular

data indicate.

The Rosenstock site provides the most evidence of any of the

Montgomery Complex sites for seasonal indicators other than deer. Four

migrating birds, present only in the winter, were identified in the Rosenstock

assemblage. In addition, Wild Turkey comprise 55% of the MNI for birds from

this site. Turkey, which are easiest and most productively hunted in the fall or

early winter, in combination with the other winter birds are 64% of the birds in

this assemblage. It appears then that, although birds were hunted year-round

at the site, they were hunted most extensively when they were largest and the

most productive (in the fall) or, in the case of the migrating birds, as they

became available in the area. The data from the fish remains indicate a similar

pattern. Much of the assemblage consists of species that could be caught

year-round, but there is the presence of species that would be available only on

a seasonal basis in the spring during spawning periods.

Very little data on seasonality was recovered from the Luray Focus

assemblages. Only three deer mandibles were recovered from the Hughes site

that indicate seasonality. One of these was from the fall and two from the

spring. Three intact deer antlers as well as the presence of one Whistling

Swan indicate additional hunting in the fall or winter. Although these data are

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limited, what is most interesting is not the presence of certain data but the

absence of other data. The absence of seasonally available fish or more

seasonally available birds is significant. I do not think that this lack of birds and

fish is due to sampling at the site. The faunal material from both sites was

excavated and screened in a similar manner and only the screened samples

from both sites were analyzed for this study. Rather, this absence indicates

that unlike the occupants of the Rosenstock site, the occupants of the Hughes

site were not necessarily hunting these very productive resources as they

became available throughout the year. What can be concluded is that hunting

was occurring year-round, but, unlike the pattern observed at the Rosenstock

site, seasonally available resources were not so deliberately targeted and

scheduled into the annual round of activities. When seasonally available

resources were included in hunting, they were almost incidental and not part of

a larger effort to maximize their availability.

Animal Selection, Processing, and Butchering

The distribution of skeletal elements and the distribution of various types

of butchering scars both provide sufficient quantities of data to make general

comparative statements between the two complexes. Figure 15, shows that the

distribution of deer skeletal elements at these two sites are both similar to each

other and different from the standard deer. Both assemblages are slightly

elevated in all limb categories and suppressed in the axial category. The

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Percentages of Deer MNE by Body Part O \J C - j i o o D < o CO o o O o 06e}U0Ojed 264

Figure 15 265

conclusion drawn from these data is similar for both sites - there was probably

some degree of carcass preparation in the field away from the village, most

likely at the hunting site. The butchering data from the two sites are also

similar, with the most frequent activities being dismemberment, filleting, and

marrow extraction.

Conclusion

The data presented and tested in this chapter indicate that the hunting

strategies associated with the two archaeological complexes under study differ

in four very important ways: in the diversity of animals being hunted and

collected; in the habitats that were being exploited; in the focus on seasonal

resources; and, with deer, in the hunting of specific age classes of individuals.

In the Montgomery Complex, as evidenced by data from all three sites, hunting

was occurring year-round with seasonally available resources being targeted for

exploitation as they became available. Hunting was not limited to specific

animals but rather took advantage of available resources from every

surrounding habitat, both aquatic and terrestrial. Finally, the data on deer

hunting differs between the Rosenstock and the Winslow sites. At the

Rosenstock site, the individuals that had the most meat available, the full-sized

males, were being specifically targeted. At the Winslow site, however, it was

the older and the younger individuals that were hunted, those individuals that

could be killed with the least amount of hunting time invested.

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In contrast, in the Luray Focus, as evidenced primarily by data from the

Hughes site and supported by limited data from the Keyser Farm and Shepard

Barrack site assemblages, although hunting was occurring year-round, only a

limited variety of animals were being hunted and collected. These were mostly

deer, turkey, and turtles with other animals almost incidental in the overall

hunting strategy. Seasonally available resources were hunted occasionally but

were not targeted and utilized as fully as they were in the earlier Montgomery

Complex, nor were animals from all habitats being exploited. The broad variety

of other animals that were certainly available at these sites were not being

hunted, or if they were, their remains were not being deposited in the village

trash or storage pits. Finally, although deer were the most frequently hunted

animal at these sites, as at the Rosenstock site, older individuals were being

targeted. Unlike the pattern at the Rosenstock site, however, very few

individuals in the younger age classes (less than one-year and one-to-two

years) were killed. While the Rosenstock site had a deer age composition

curve that was similar to the natural population except for the elevation in

middle-aged individuals (Figure 6), the deer age composition curve from the

Hughes site does not resemble the natural population at all (Figure 11).

Instead, the distribution at the Hughes site has most of the individuals in the

most productive two-to-five year old age classes. There are at least two

possible reasons for this predominance of the middle-aged individuals. One of

these is that these age classes were being deliberately chosen because they

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were the most productive for meat return. Another possible reason is that the

killing of these age classes is the result of the hunting technique being used.

Using certain hunting techniques will result in different age curves. More detail

on the relationship between hunting techniques and the age composition of the

individuals being killed will be discussed in the concluding chapter.

There are several possible reasons for the overall differences in the

hunting strategies between the Montgomery Complex and the Luray Focus.

These possible reasons and the implications of these differences will be

discussed in the concluding chapter.

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CONCLUSIONS

Introduction

The main goal of this research has been to examine sociocultural

differences between two Late Woodland archaeological cultures, the

Montgomery Complex and the Luray Focus, as reflected in the hunting

strategies of these two cultures. This examination has been done with the

zooarchaeological analysis of the vertebrate faunal assemblages from six sites.

From the Montgomery Complex, assemblages were examined from the

Rosenstock site, the Shepard site, and the Winslow site. The Rosenstock site

provided the majority of the data from the Montgomery Complex. While the

Rosenstock site has been classified as a Montgomery Complex site, there are

some differences between this site and the Shepard and Winslow sites which

may make Rosenstock atypical for the Montgomery Complex. Some of these

differences include site size, site organization, and distribution of radiocarbon

dates. These differences have not yet been fully examined by the site

excavators and the results of the analysis of the artifacts and features at

Rosenstock may have further implications for the interpretation of the faunal

268

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assemblage. The acknowledgement that Rosenstock may be anomalous for

the Montgomery Complex does not discount the current research and

interpretations. It does, however, allow that factors other than the ones

examined here may account for some characteristics of the faunal data.

From the Luray Focus, assemblages were examined from the Hughes

site, the Keyser Farm site, and the Shepard Barrack site. The Hughes site

provided the majority of the data from the Luray Focus. This was

supplemented by the data from the Keyser Farm and Shepard Barrack sites.

The long-term prehistory of this area is frequently described in terms of a

trajectory of increasing socio-political complexity in combination with changing

resource procurement strategies. This can be seen on a very broad level by

examining the traditional subdivisions for the long-term prehistory of the region

and how these are defined and distinguished from each other. The first

inhabitants of the region, Paleoindians, are described as small groups of

nomadic hunters and gatherers who utilized a variety of both large and small

animals as well as a variety of fish and plant resources. The subsequent

Archaic period is defined primarily through its exploitation of a broader resource

base as well as specializing in the exploitation of the particular resources of

local areas. Groups during the Archaic remained widely dispersed in small,

mobile bands.

The Woodland period, the threshold of which is often defined artifactually

by the presence of ceramics, was a time of population growth and the

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appearance of an increasingly sedentary way of life. Permanent villages were

accompanied by outlying specialized extraction camps for the procurement and

processing of a variety of resources. The Woodland period is also

characterized by the introduction of cultivated plants and the increasing use and

investment of time and energy into the production and processing of these

cultivars. By the time of European contact, the Lower Potomac Valley and

many of the surrounding areas throughout the region were part of a series of

chiefdoms. The inhabitants participated in a highly organized society - one in

which the exploitation of available local resources and the cultivation of plants

played important roles in the subsistence economies. Both plants and animals,

as well as other resources, were included in a redistribution of goods by the

chief, and villages were expected to produce not only enough food for their own

use but also enough to contribute to the redistributive process. This backdrop

of increasing sociocultural complexity provides the context for this research.

The Research Question

The specific placement of the Montgomery Complex and the Luray

Focus in the broad continuum of sociocultural change outlined above is not yet

completely understood. A complex social structure including the year-round

occupation of villages and the cultivation of plant foods was certainly

established at the time of the occupation of the sites examined above, but the

extent to which the local subsistence economies depended upon those

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cultivated goods is not clear, and it will be discussed more below. One major

assumption that is critical for this study is that this dependence upon cultivated

goods was increasing over time. This increase was not necessarily progressing

at a steady pace nor was it progressing in a predictable manner. Indeed, there

could have been long periods of stasis interspersed by short- or long-term

periods of change. These periods of change also do not have to have been

unidirectional. There could have been periods where the commitment to

cultivation was decreasing and not just periods where it was increasing. As

discussed earlier, a systemic approach to the explanation of cultural change

assumes an interactive relationship between all aspects of a given cultural

system. This approach does not attempt to assign causality to any one of

these aspects nor does it take a simplistic evolutionary perspective that all

cultures are constantly moving towards increasing complexity. While, from a

long-term perspective there is an increase in sociocultural complexity in the

region, studies, including this one, examining shorter periods of time cannot

always assume that change is occurring during that particular period of time.

In Chapter One, it was postulated that if there was an observable

difference in the hunting strategies between the two archaeological cultures

under examination, then it is possible that this was due to a change in the

dependence upon cultivated foods between the Montgomery Complex and the

Luray Focus. A number of models have been developed to describe changes

in hunting strategies that have occurred in horticultural economies as those

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economies become increasingly committed to cultivating plants. One of these

responses is a focus on both small and large mammals that feed on cultivated

plants and that are immediately available with a minimum of hunting time

invested, known as garden hunting (Linares 1976). An alternative model

developed by Speth and Scott (1989) includes a shift to hunting primarily those

animals with a high return regardless of whether those animals are available

locally or require travel of relatively long distances to acquire. Although this

strategy frequently requires great amounts of time and energy, the return is

considered worth the investment. These models, when applied to contexts

other than those for which they were developed, are not necessarily mutually

exclusive. A combination of both of these adaptations, as well as numerous

possible others, could have been used by various archaeological cultures as

they incorporated horticultural and/or agricultural production into their

economies.

After examining these alternative models, three possible responses for

the situation under examination by this research were defined and it was

hypothesized that if there was an increase in cultivation then one of these

responses may have occurred in the study area. The first of these responses

is a concentration in the use of selected animal species, possibly the more

productive ones as more time was needed to tend crops. These species could

also be the ones that were feeding in the fields or were immediately available in

the river - animals that could have been hunted or collected with a minimum

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amount of time spent away from the immediate village area. The second

response discussed was a complete restructuring and rescheduling of animal

procurement strategies, shown through changes in seasonal scheduling of

hunting forays as certain times of the year became devoted to agricultural

tasks. This restructuring could also be reflected as a change in which more

localized resources were being hunted more intensively to again reflect the time

constraints necessitated by agricultural tasks. Finally, it was proposed that

there could be no evident change in hunting patterns between the two cultures,

the result of the already existing hunting strategies being flexible enough to

accommodate a variety of sociocultural changes, whether these changes

included an increased dependence upon agriculture or not.

The data collected through the faunal analysis and presented in Chapter

Five can be used to address which differences occur between these two

archaeological complexes. There is a distinct difference in hunting strategies

between the Montgomery Complex and the Luray Focus. During the

Montgomery Complex, hunting a large variety of animals from many habitats

was occurring throughout the year at all of the sites examined. Deer, the most

important animal in the diet, were hunted with a specific strategy at the

Rosenstock site, a strategy that maximized meat return for time and effort put

into hunting. The individuals that were of maximum meat-yielding age and size

were the ones more frequently hunted while individuals from other age groups

were hunted more proportionately to their distribution in a natural population. At

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the Winslow site, the strategy for deer hunting was just the opposite, with

younger and older animals being taken more frequently than the prime-aged

two-to-three year olds. Finally, during the Montgomery Complex, seasonally

available resources such as fish and migrating birds were targeted for

exploitation as they became available. As an overall pattern, the occupants of

these sites appear to have been maximizing the exploitation of many, if not all,

of the animal resources found in the area.

During the Luray Focus, in contrast, although hunting was occurring

throughout the year, only a limited number of taxa were being hunted. Those

animals were the ones that were probably found feeding in the fields. Few

aquatic species were utilized although the site location is ideal for the collection

of them. Indeed, given the Hughes site's proximity to the Fall Line, it is likely

that several species of large anadromous fish would have been available at

least on a seasonal basis during spawning runs. The deer that were killed

were primarily those in the two-to-five year-old age classes, with very few

individuals being represented in the younger age classes. Finally, seasonally

available resources were hunted or collected only incidentally at the sites in the

Luray Focus and there appears to be no shifting of time and energy to utilize

these resources that were available in large quantities for limited amounts of

time throughout the year.

Given these differences in hunting strategies between these sites, it can

be seen that the first of the three responses suggested earlier appears to be

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most applicable. This response was defined as a concentration in the use of

selected productive species. The species being focussed on in this case not

only have a relatively large body weight relative to the other available animals

in their class, but can also be found in gardens or garden borders.

One of the implications for a pattern of garden hunting calls into question

the frequently held view of a gender-based division of labor in prehistoric

societies with men performing hunting and women performing gardening. If

women are performing most of the gardening tasks, then they would often be in

an opportune position to hunt those animals frequenting the gardens and

garden borders. Given the hunting pattern in the Luray Focus, it is very

possible that women were performing as much hunting as men. Indeed, given

the presence of palisades and the presence of defense and warfare that these

imply, it is possible that women were performing most of the hunting as well as

the gardening while the men were involved in defensive activities.

It was hypothesized earlier that it may be possible to determine whether

the groups from these two complexes are horticultural or agricultural given the

zooarchaeological data. This determination has implications for the

examination of other aspects of the sociocultural system. As defined earlier,

horticultural economies are those where people are deliberately planting and

harvesting cultivars, are depending on these foods as a relatively predictable

resource, but continue to follow previously developed strategies of hunting,

fishing, and collecting a variety of plant and animal resources, whether those

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resources are acquired throughout the year or on a seasonal basis. Activities

associated with the planting, care, and harvesting of cultivars become

incorporated into the already established seasonal cycle of activities. While

associated sedentism is possible with horticultural economies, it is not required.

Villages occupied on a year-round basis could be located near the fields with

various hunting and collecting forays emanating from this central base, or

visiting the field location could simply be another stop on a more nomadic

seasonal round of procurement of a variety of resources.

Agricultural economies, in contrast, have incorporated cultivation related

activities to the point that previously developed subsistence activities are

changed or abandoned to accommodate the limited amount of time and energy

remaining after agricultural activities are completed. For numerous possible

reasons, from providing food to participating in a sociopolitical redistribution of

prescribed resources, the production of these cultivated plants has become

increasingly important. Sedentary villages are necessary to maintain enough

people throughout the year to plant, care, protect, and harvest these resources.

Other food related activities become scheduled as time is available, time which

is not necessarily the most optimal when examining the potential return of the

resource. For example, clearing fields and planting crops occurs in the spring,

the same time that anadromous fish are spawning and available in the largest

quantities throughout the year. Although occasional anadromous fish could be

collected prior to or following the cultivation related activities, they could not be

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netted in such large quantities in as short amount of time as they can during

spawning runs. A choice must then be made to invest ail energy available at

that time to clearing and planting or to divide energy between maximizing fish

collecting and planting possibly a smaller area.

Given these definitions, little to no alteration of previously existing

hunting strategies and seasonal activities can be considered indicative of

horticulture and an increasing alteration or total disruption of hunting strategies

and seasonal activities can be considered indicative of agriculture. The

zooarchaeological data indicates that the archaeological cultures examined in

this study fit at very different locations in the socioeconomic continuum from

horticulture to agriculture. The Montgomery Complex, with its intensive

utilization of all animal resources in the immediate area, has a pattern closer to

the horticultural end of this spectrum. The Rosenstock site is located on a bluff

above the east bank of the Monocacy River. Across the river on the west side

is a floodplain area with fertile soil, the area most probably used as fields.

There is no available fertile land on the east side of the river where the village

is located but the river is easily passable at the location of the Rosenstock site

(Kavanagh, personal communication 1993). The Winslow and Shepard sites

are both located immediately adjacent to the Potomac on well-drained, deep

floodplain Huntington silt loam soils.

The Luray Focus, with its less intensive hunting pattern of acquiring the

most convenient resources, is closer to the pattern expected for an agricultural

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economy. The Hughes site is located approximately 300 feet north of the north

bank of the Potomac River in the floodplain environment. The site is above the

Fall Line in the Piedmont province in Montgomery County, Maryland. The

village itself is located on Huntington silt-loam, soils considered the most fertile

and productive for agricultural growth in the county. Immediately adjacent to

the river and behind the site in a wetland area approximately 250 feet from the

site is a more poorly drained soil series that is frequently flooded. It is not

known if the wetland area to the north of the site was a wetland at the time of

the Hughes site occupation. It is possible that it was an active channel of the

Potomac at that time (Dent and Jirikowic 1990:6). Either way, it would have

been unusable as an occupational area. If this area was a wetland, it could

have provided an area attractive to many terrestrial and aquatic species of

animals. If it was an active channel, it could have provided another area for

fishing and collecting a variety of aquatic resources. Because the Hughes site

is close to the Fall Line it would not be surprising if anadromous or marine

species of fish were recovered in the assemblage given the site's proximity to

the river. The lack of these species is significant and illustrates even more

dramatically how non-intensive the hunting and fishing strategies at this site

were.

It is possible that the observed difference in hunting strategies could be

due to other sociocultural factors besides a change in dependency on cultivated

goods. This response leads to further questions about the broader sociocultural

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contexts of the Late Woodland and why these strategies differ between these

two cultures.

Besides hunting strategies, one of the major differences between the two

cultures under question is the presence of a palisade in the majority of the later

Luray Focus sites. Gramly (1988) states that "The appearance of the first

fortifications, rather than trauma on skeletons caused by armed violence, is the

better guide for determining when organized conflict became a fact of life for

the Indians of the Eastern Woodlands" (Gramly 1988:91). Gramly goes on to

hypothesize that the primary reason for conflict in the Eastern Woodlands was

competition for deer skins.

Given the limited sustainable yield of wild animal hides from the forests of the East (Gramly 1977) and given a growing population fed by maize, it was inevitable that conflicts should have culminated in feuding, killing, and outright usurpation of hunting territories belonging to groups who were defeated in wars. As a defense against surprise attack, fortifications would have been erected in remote places with difficult access (Gramly 1988:91).

While competition for deer skins may have been one factor in the

appearance of fortifications in the study area, I do not think that it is the only

one. One reason is that the Luray Focus sites under question are not "in

remote places with difficult access" but are located bn major waterways with

immediate access to anyone using those waterways to travel throughout the

region. The second reason is that if deer were a scarce commodity, or even if

deer were just decreasing in population, then a more intensive hunting pattern

for deer would be expected, one that exploited large numbers of deer from all

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age classes, not a less intensive pattern as seen in the Luray Focus.

As seen earlier in the discussion of the cultural history for the region,

there is considerable evidence that indicates that the Luray Focus may be a

southern intrusion of the Monongahela culture. If this is so, then it should not

be surprising that there would be fortifications at the sites of a culture, the Luray

Focus, that is expanding into a previously occupied area, in this case,

occuppied by the Montgomery Complex. This presents another question,

however, which is why does the Hughes site appear not to have been

palisaded? It is within a mile of two major Montgomery Complex sites, the

Shepard and Winslow sites. If those sites were occuppied at the time of the

establishment of the Hughes site, then one would expect that the Hughes site

would be palisaded. Given the distribution of radiocarbon dates at all three of

these sites (Table 1), it is possible that the Shepard aand Winslow sites were

occuppied prior to the establishment of the Hughes site and that all three of

these sites were not contemporaneous, even for a short period. Further

excavations at the Hughes site may be able to address these issues.

This southern movement as described above would also explain the

location of Luray Focus sites on major waterways. As people moved

southward, they most likely travelled along the water and, since they were

coming with an economy that included the cultivation of domesticated plants, it

would make sense to stay along the rivers where the prime agricultural land

was located. In addition, if there was trade or continuing contact throughout the

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region, being located on a large river provides immediate access to a major

means of transportation and other people who may be using that route.

Waselkov (1978) hypothesized about changes in hunting strategies, how

they are reflected in the zooarchaeological record, and their relationship to

sociocultural complexity. Waselkov divided various hunting strategies known in

the ethnohistorical record for Virginia into two main types, stalking and

communal driving. Stalking would result in an acquisition pattern of young deer

(yearlings and under) and old deer (over 4 1/2 years), giving a bimodal age

distribution (Waselkov 1978:22). Communal driving, in contrast, would result in

a unimodal age distribution, with all age classes represented archaeologically

relative to their distribution in a living population (Waselkov 1988:20-21).

Waselkov then examined the deer age data from a series of prehistoric sites in

light of the expected patterns for the two types of hunting methods. He found

that sites from earlier tribal-level societies had a bimodal (stalking) distribution

of ages while later chiefdom-level Mississippian societies had a unimodal

(communal drive) age distribution. In addition, these later societies were large

fortified villages closely spaced in the bottomlands of major rivers, putting stress

on the local deer population. Waselkov concludes that:

Carefully coordinated, seasonally scheduled deer drives would have been the most effective means of harvesting a limited resource. The Middle Mississippians had achieved a chiefdom level of socio-political organization; that is, they had redistributional societies with permanent central agencies of coordination (Service, 1971: p. 134). This conclusion is based on comparisons with flourishing Mississippian-derived societies, such as the Natchez, observed by early European visitors, as well as from archaeological evidence for hereditary ranked status (e.g., Larson,

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1971: p.67; Peebles and Kus, 1977:pp.435-40). It seems reasonable to hypothesize that concomitant with the increase in social complexity was an elaboration of subsistence methods, specifically the intensified exploitation of selected species (cf. Smith, 1975: p. 139) (Waselkov 1978:23).

An exception to this pattern is in the data from a series of sites where

the occupants were involved in the fur trade. At those sites, communal drives

were being used even though the societies were tribes and not chiefdoms. In

these cases, however, Waselkov claims that it was the introduction of an

additional external variable, the pressure to acquire deer skins for trade, that

provided the stimulus for adopting a more intensive exploitation pattern.

Smith (1975) proposed a different pattern for stalking in the fall. One of

the historically documented techniques used by Eastern Indians in stalking

involved the use of a decoy. The decoy consisted of a hunter with a set of

antlers or a deer skull with a deer skin. The hunter would hide in the bushes,

rustling the branches to make noise. In the fall, male deer are in rut and are

more curious than at other times of the year. When the deer investigated the

rustling noises, they became more vulnerable to the hunter and were then killed

(Smith 1975). Using this technique would result in a killing pattern of primarily

adult male deer.

If we apply Waselkov's pattern of stalking as indicative of a tribally

organized society and communal drives as indicative of a chiefdom, then it

appears that both the Montgomery Complex and the Luray Focus are probably

both tribal-level societies. The patterns of the deer age data from the

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Rosenstock and Winslow sites are bimodal distributions. The Rosenstock site

has one elevation in the very young (under one-year) age class and another in

the three-to-five year-olds, the age class at its prime meat weight (Figure 6).

The Winslow site has its two elevations in the very young (less than one-year)

and the very old (over five years) age classes.

As stated before, the Hughes site has most of its deer in the two-to-five

year-old age classes with very few in the young or older age classes. This

distribution has very little resemblance to a natural population. As discussed

earlier, it is the similarity of the unimodal distribution of individuals in the

archaeological assemblage to a natural population curve that indicates the

presence of communal drives. This pattern at the Hughes site indicates that

stalking is probably occurring, but possibly with a different technique than at the

Rosenstock and Winslow sites. One artifact in particular may be an indicator of

this technique. At the Keyser Farm and Miley sites, possible antler

headdresses were recovered. Although it is possible that these were used for

ceremonial purposes, it is also possible that they could have been used as

hunting decoys. If this is so, and if this is a trait of Luray Focus culture in

general, and not specific to the Keyser Farm and Miley sites, this could indicate

decoy stalking which would account for the age composition of deer at the

Hughes site.

The possible use of stalking for deer hunting does not discount the

previously hypothesized presence of garden hunting. Different hunting

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techniques could have been used for different species, especially if those

species have different behaviors. It is also possible that both opportune garden

hunting and deliberate stalking could have been used at the same site for the

same species, in this case, deer. While garden hunting may have provided a

relatively steady source of meat while there was food in the fields to attract the

animals, this would not necessarily have provided all of the meat needed

throughout the year. For those instances when garden hunting was not

sufficient, stalking could have been used as a supplemental hunting technique.

It is also possible that at some sites stalking provided the majority of the deer

killed while garden hunting was the more supplemental hunting technique. In

either case, the use of more than one hunting technique would have increased

the possibility of hunting success.

In conclusion, the answer to the basic research question posed here of

"is there a difference in the hunting strategies between the Montgomery

Complex and the Luray Focus given the zooarchaeological data from six sites

from these two archaeological cultures," is yes. Yes, there are some very

distinct differences in hunting strategies between these two cultures.

Furthermore, given the cultural historical context of these sites, there are

several sociocultural factors which could have affected the hunting strategies or

which can be used to explain the differences in hunting strategies between

these two cultures.

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The Use of Curated Collections

As discussed in Chapter One, one additional issue to be addressed by

this research is the relative completeness and research applicability of the

curated assemblages. These assemblages, recovered up to 40 years ago,

were examined using a series of indices and criteria designed to evaluate their

representativeness of the archaeological record. This examination was done by

comparing this series of indices from the curated assemblages to the same

indices from recently excavated assemblages. The results of this examination

are encouraging. The analysis of these assemblages indicates that, although

they were not complete enough to yield all of the data necessary to answer all

of the research questions being addressed here, these assemblages did fit very

well into the broad patterns and conclusions that were reached using the

primary material. In addition, the bone tool sample in some of these

assemblages is fairly high and a study of bone tools from the two

archaeological complexes would be feasible using these samples.

The implications of these conclusions for research based on the analysis

of other artifact classes is also encouraging. While studies of debitage would

probably not be feasible, the formal stone tool collection should be relatively

representative. Likewise, an analysis of ceramic remains would probably yield

a high percentage of diagnostic {i.e., rim, handle, or shoulder) or unique sherds

rather than a representative sample of body sherds. Since recovering a variety

of the faunal remains was one explicit goal for some of the excavations of these

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sites, this emphasis toward recovering representative variety may also be

present in the ceramic and lithic material.

One artifact class that probably did not fare as well as the others in

these earlier collections is the archaeobotanical remains. While larger

specimens such as corn cobs, kernels, or larger seeds and pits recovered at

most of these sites, smaller specimens were only collected at the two primary

sites. Botanical samples are even more biased by a lack of screening and

flotation than the faunal remains since a larger proportion of botanical remains

are so small. An examination of the archaeobotanical sample from the curated

assemblages may indicate the presence of domesticates but it is doubtful that a

comparison of the proportions of cultivated plants versus wild plants utilized at

the site could be performed. Since ethnobotanical evidence could be critical to

providing further data to address the arguments and conclusions in this

research, the ethnobotanical samples from the primary assemblages become

even more important.

Directions for Future Research

There are a number of directions that future research related to or

building upon the results of this research could move into. The most obvious of

these is analyzing the archaeobotanical evidence from these sites. This

analysis could be used to determine what the patterns of plant exploitation are

and if these patterns mirror or correspond in some way to the patterns revealed

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by the examination of the zooarchaeological material. The most directly related

question would be whether or not there appears to be an increase in the

amount of time and energy devoted to cultivation for this particular period in

time. The results from the archaeobotanical analysis, in combination with the

results from the zooarchaeological analysis could then be used to create a

more complete picture of changing subsistence systems. These systems may

include an increase in the commitment to cultivation or they may include other

changes that could be indicated by the archaeobotanical analysis that are not

obvious from the zooarchaeological analysis. This combination of

zooarchaeological and archaeobotanical data could yield a more complete

model of subsistence change, one that may be general enough to apply to

other cultural contexts where agricultural development is occurring.

Another issue related to this research is when did cultivation first become

present in the region and how did this initial introduction of cultivation affect

hunting strategies? Again, the first part of this question would be answered

primarily with archaeobotanical data. Examining the zooarchaeological data

from sites over a lengthy time span would be necessary to determine hunting

patterns prior to cultivation and how hunting strategies in general changed over

a longer period of time. By having this long-term description of hunting

strategies, the patterns observed at the Montgomery Complex and the Luray

Focus could be placed in a more detailed perspective. This would yield more

accurate interpretations about the relationships between many of the aspects of

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these societies that were changing for long periods of time. These aspects

include, but are not limited to, sedentism, socio-political complexity, cultivation,

and hunting strategies. The examination of village development, individual

structure size and function, and social complexity would provide a much more

complete picture of these important relationships.

On a more detailed level, two specific research questions that could be

addressed to expand upon the current results are: what were the hunting

strategies immediately prior to the Montgomery Complex; and what were the

hunting strategies for the Mason Island Complex? Answering these questions,

in combination with the broader long-term developmental questions proposed

above would provide a more detailed picture of this particular point in time.

Additional non-zooarchaeological data that could be critical to these

interpretations would be clarifying the absolute and relative chronologies of

these sites. The range of radiocarbon dates for these sites is confusing at best.

In addition, further excavations at the Rosenstock site could yield structure

outlines and pit patterns that could be used to infer information about the social

structure at the site.

Another related research question to be addressed is what are the

hunting strategies at Monongahela sites and how do these compare to those at

Luray Focus sites? There may also be indicators of ethnicity, such as

butchering patterns, that could be used to examine the relationship between the

Monongahela and the Luray Focus cultures. Examining this connection could

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have a direct impact on current discussions of the culture history of the Middle

Atlantic region.

Other future research that could be performed with these same

assemblages is an examination of bone tool production and technology at

Montgomery Complex and/or Luray Focus sites. As we have seen from the

results of the evaluation of the curated assemblages, the bone tool samples for

many of these sites appear to be relatively complete. More detailed analysis of

these tools could provide information not only on how these tools were made

but what they may have been used for.

In conclusion, the results from this research have provided data about

the changes in hunting strategies for a relatively short period of time in the

prehistory of the Potomac Valley. These results have been used to develop

hypotheses about related changes in these cultures, specifically, the possible

increasing commitment to the cultivation of plants. These hypotheses can be

tested with the analysis of other artifact classes. This research provides a

building block, one that can be used to answer broader anthropological

questions about not only how but also why cultures change.

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TABLE 23

TAXONOMIC CLASSIFICATION OF SPECIES RECOVERED

290

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Sternotherus Rana Chelydra serpentina Chelydra Chrysemys picta picta picta Chrysemys Terrapene Carolina Bullfrog: Bullfrog: catesbeiana Turtle Musk Common (Stinkpot): odoratus Turtle: Painted Eastern Softshell: Spiny Eastern Turtle: Box Eastern Carolina spinifera Snapping Turtle: Snapping Apalone spinifera Apalone

(Toads) (Coral Snakes) (Coral TABLE TABLE 23 Testudinidae Trionychidae Chelydridae Kinosternidae Emydidae Elapidae Bufonidae Ranidae Family: Family: Family: Family: Family: Family: Family: Family: Family: Family: Family: Family: (Lizards) TAXONOMIC CLASSIFICATION OF SPECIES RECOVERED Cryptodira Lacertilia Serpentes Squamata Anura Sub-Order: Sub-Order: Sub-Order: Chelonia Sub-Order: Reptilia Amphibia Order: Order: Order: Order: Order: Order: C lass: C lass:

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Buteo Corvus Olor Gavia Bonasa Meleagris

Colinus virginianus Colinus umbellus Ectopistes migratorius Ectopistes Woodpecker: Pileated Common Loon: Loon: Common immer columbianus Grouse: Ruffed Common Bobwhite: Common Passenger Pigeon: Passenger Dryocopus pileatus Dryocopus Woodpecker: Red-Bellied carolinus Melanerpes brachyrhynchos gallopavo Wild Turkey: Turkey: Wild American Crow: Crow: American jamaicensis Hawk: Red-Tailed (Geese) Swan: Whistling (Mergansers) Cygninae Merginae Buteoninae Anserinae Sub-Family: Sub-Family: Sub-Family: Sub-Family: Sub-Family: Sub-Family:

Continued TABLE 23 TABLE Corvidae Gaviidae Tetraonidae Columbidae Phasianidae Meleagrididae Picidae Anatidae Accipitridae Family: Family: Family: Family: Family: Family: Family: Family: Family: Family: Family:

Columbiformes Gaviiformes Galliformes Piciformes Passeriformes Falconiformes Anseriformes Aves Order: Order: Order: Order: Order: Order: Order: Order: Order: Order: C la ss :

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Luxilus

Anguilla Semolitus Nocomis Cyanocitta Catostomus commersoni Catostomus Quiscalus quiscula Quiscalus River Chub: Chub: River comutus Sucker: Hog Northern nigricans Hypentelium Moxostoma cristata Creek Chub: Chub: Creek micropogon Chub: Mouth Big platyrynchos Nocomis Shiner: Common Blue Jay: Jay: Blue atromaculatus macrolepidotum Common Grackle: Common rostrata Shorthead Redhorse: Shorthead White Sucker: White American Eel: Eel: American

(Trouts and Allies) and (Trouts Continued TABLE 23 TABLE Catostomidae Cyprinidae Icteridae Salmonidae Anguillidae Family: Family: Family: Family: Family: Family: Family: Family: Family:

Cypriniformes Salmoniformes Anguilliformes Osteichthyes Order: Order: Order: Order: Order: C la ss :

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Lepus

Morone Marmota

Tamias striatus Tamias Sylvilagus iloridanus Sylvilagus Eastern Cottontail: Eastern Chipmunk: Eastern Squirrel: Gray Eastern carolinensis Sciurus Squirrel: Fox Eastern niger Sciurus Moxostoma erythrurum Moxostoma americanus monax Golden Redhorse: Golden anisurum Moxostoma Bullhead: Brown saxatilis Striped Bass: Bass: Striped Snowshoe Hare: Hare: Snowshoe Woodchuck: Woodchuck: Silver Redhorse: Silver Ameirus serracanthus Ameirus

(Sunfishes)

Continued TABLE 23 TABLE Centrarchidae Sciuridae Ictaluridae Moronidae Leporidae Family: Family: Family: Family: Family: Family: Family: Sciuromorpha

Rodentia Siluriformes Perciformes Lagomorpha Sub-Order: Sub-Order: Mammalia Order: Order: Order: Order: Order: Order: Order: C lass:

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Felis Mephitis

Lutra sp. Erethizon Urocyon

Vulpes fulva Vulpes Ondatra Castor Lynxrufus Mustela vison Mustela Canis familiaris Canis V. V. vulpes) Beaver: Beaver: canadensis Peromyscus Muskrat: dorsatum concolor Bobcat: cinereoargenteus frenata Mustela Mink: Otter: River canadensis Mouse (unspecified): Mouse Porcupine: Lion: Mountain Dog: Red Fox: (also Fox: Gray Longtail Weasel: Longtail Skunk: Striped mephitis zibethica

Continued TABLE 23 TABLE Castoridae Cricetidae Canidae Erethizontidae Felidae Mustelidae Family: Family: Family: Family: Family: Family: Aeluroidea Arctoidea Myomorpha Hystricomorpha Carnivora Sub-Order: Sub-Order: Sub-Order: Sub-Order: Sub-Order: Sub-Order: Order: Order:

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Cervus Ursus Procyon lotor Procyon Odocoileus virginianus Odocoileus canadensis Raccoon: Raccoon: (Wapiti): Elk Black Bear: Bear: Black americanus White-tailed Deer: White-tailed

Continued TABLE 23 TABLE Ursidae Cervidae Procyonidae Family: Family: Family: Ruminantia Artiodactyla Sub-Order: Sub-Order: Order: Order:

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TABLE 24

HABITATS FOR SPECIES RECOVERED

297

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TABLE 24

TAXONOMIC CLASSIFICATION OF SPECIES RECOVERED

Class: Amphibia Family: Bufonidae (Toads) Habitat: Requires shallow bodies of water to breed, hiding places with moisture, and an abundant supply of insects and other invertebrates for food (Conant and Collins 1991:306-307).

Family; Ranidae Habitat: Aquatic, including streams, rivers, and lakes (Conant and Collins 1991:335).

Bullfrog: Rana catesbeiana Habitat: Aquatic and preferring larger bodies of water than most other frogs. Lives in lakes, ponds, bogs, sluggish portions of streams, etc. Small streams are also utilized when other habitats are lacking (Conant and Collins 1991:335-336).

Class: Reptilia Snapping Turtle: Chelydra serpentina Habitat: Lives in any permanent body of fresh water, large or small, occasionally brackish water. Omnivorous, food includes small aquatic invertebrates, as well as a variety of vertebrates and vegetation (Conant and Collins 1991:41-42).

Common Musk Turtle (Stinkpot): Sternotherus odoratus Habitat: Abundant in many bodies of water, but not often observed except in shallow, clear-water lakes, ponds, and rivers. Prefers still waters (Conant and Collins 1991:44).

Eastern Painted Turtle: Chrysemys picta picta Habitat: Lives chiefly in shallow water with profuse aquatic vegetation and soft and muddy bottoms of ponds, marshes, ditches, edges of lakes, backwaters of streams, and river pools (Conant and Collins 1991:71).

Eastern Spiny Softshell: Apalone spinifera spinifera Habitat: A river turtle but also lives in lakes and other quiet bodies of water where sand and mud bars are available (Conant and Collins 1991:79-80).

Eastern Box Turtle: Terrapene Carolina Carolina Habitat: Essentially terrestrial but occasionally soak themselves in mud

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TABLE 24

Continued

or water. Burrow beneath logs or rotting vegetation (Conant and Collins 1991:52-53).

Sub-Order: Lacertilia (Lizards)

Family Elapidae (Coral Snakes) Habitat: Extremely poisonous snakes that live in wooded areas and hide under leaves or debris. Habitats vary from well-drained woods and open, dry, sandy areas to pond and lake borders (Conant and Collins 1991:224).

Class: Aves Common Loon: Gavia immer Habitat: Wooded lakes, tundra ponds (summer), coastal waters. In Middle Atlantic region in winter (Peterson 1980:32).

Whistling Swan: Olor columbianus Habitat: Lakes, large rivers, bays, estuaries, flooded fields. In Middle Atlantic region in winter (Peterson 1980:42).

Geese: Sub-Family Anserinae Habitat: Waterfowl, more terrestrial than ducks, grazing on land. In Middle Atlantic region in winter (Peterson 1980:42).

Mergansers: Merginae Habitat: Waterfowl, Lakes, ponds, rivers. In Middle Atlantic region in winter (Peterson 1980:62).

Red-Tailed Hawk: Buteo jamaicensis Habitat: Open country, woodlands, prairie groves, mountains, plains. Resident year-round (Peterson 1980:154).

Ruffed Grouse: Bonasa umbellus Habitat: Ground and understory of deciduous or mixed woodlands. Resident year-round (Peterson 1980:144).

Common Bobwhite: Colinus virginianus Habitat: Brushy open country, roadsides, wood edges. Resident year- round (Peterson 1980:148).

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TABLE 24

Continued

Wild Turkey: Meleagris gallopavo Habitat: Woods, mountain forests, wooded swamps. Resident year- round (Peterson 1980:144).

Passenger Pigeon: Ectopistes migratorius

Pileated Woodpecker: Dryocopus pileatus Habitat: Conifer, mixed, and hardwood forests, woodlots. Resident year- round (Peterson 1980:188).

Red-Bellied Woodpecker: Melanerpes carolinus Habitat: Woodlands, groves, orchards, towns. Resident year-round (Peterson 1980:190).

American Crow: Corvus brachyrhynchos Habitat: Woodlands, farmland, agricultural fields, river groves, shores. Resident year-round (Peterson 1980:206).

Blue Jay: Cyanocitta cristata Habitat: Oak and pine woods, groves. Resident year-round (Peterson 1980:208).

Common Grackle: Quiscalus quiscula Habitat: Croplands, groves, streamsides. Resident year-round (Peterson 1980:254).

Class: Osteichthyes American Eel: Anguilla rostrata Habitat: Catadromous species, spawns in Atlantic Ocean and ascends streams. Common near sea; uncommon in more inland streams and lakes. Usually in permanent streams with continuous flow. Hides in undercut banks and deep pools (Robins, Ray, and Douglass 1986:49).

Family Salmonidae (Trouts and Allies) Habitat: Lives in cool to cold streams and lakes. Freshwater or migrate into fresh water to spawn (Robins, Ray, and Douglass 1986:75).

Creek Chub: Semolitus atromaculatus Habitat: Lives in rocky and sandy pools of headwaters, creeks and small rivers (Page and Burr 1991:87-88).

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TABLE 24

Continued

River Chub: Nocomis micropogon Habitat: Lives in rocky runs and flowing pools of small to medium rivers (Page and Burr 1991:91-92).

Big Mouth Chub: Nocomis platyrynchos

Common Shiner: Luxilus cornutus Habitat: Lives in rocky pools near riffles in clear, cool creeks and small to medium rivers (Page and Burr 1991:110).

White Sucker: Catostomus commersoni Habitat: Wide range of habitats from rocky pools and riffles of headwaters to large lakes. Usually in small, clear, cool creeks and small to medium rivers (Page and Burr 1991:169).

Northern Hog Sucker: Hypentelium nigricans Habitat: Rocky riffles, runs, and pools of clear creeks and small rivers; occasionally large rivers (Page and Burr 1991:180).

Shorthead Redhorse: Moxostoma macrolepidotum Habitat: Rocky pools, runs, and riffles in small to large rivers; lakes (Page and Burr 1991:184).

Golden Redhorse: Moxostoma erythrurum Habitat: Mud- to rock-bottomed pools, runs and riffles of creeks and small to large rivers; occasionally lakes (Page and Burr 1991:185-186).

Silver Redhorse: Moxostoma anisurum Habitat: Mud- to rock-bottomed pools, runs and riffles of creeks and small to large rivers; occasionally lakes (Page and Burr 1991:186).

Brown Bullhead: Ameiurus serracanthus Habitat: Pools and sluggish runs over soft substrates in creeks and small to large rivers; impoundments, lakes, and ponds (Page and Burr 1991:195).

Striped Bass: Morone saxatiiis Habitat: Marine; ascends large rivers far upstream to spawn. Channels of medium to large rivers during spring spawning runs; lakes, impoundments, and connecting rivers (Page and Burr 1991:254-255).

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TABLE 24

Continued

Family Centrarchidae (Sunfishes) Habitat: Freshwater; generally in sluggish waters, pools (Page and Burr 1991:258).

Class: Mammalia Snowshoe Hare, Jackrabbit: Lepus americanus Habitat: Swamps, forests, thickets, mountains in the west. Habits: Nocturnal. Home range about 10 acres, but may travel up to 1 mile. Populations fluctuate tremendously, with highs about every 11 years. Young: Born April-August (Burt and Grossenheider 1980:205).

Eastern Cottontail: Sylvilagus floridanus Habitat: Heavy brush, strips of forest with open areas nearby, edges of swamps, weed patches. Habits: Active from early evening to late morning. Feeds on green vegetation in summer, bark and twigs in winter. Home range 3-20 acres. Populations fluctuate from 1 per 4 acres to several per acre especially in winter concentrations. Young: Born mostly March-May, also in September (Burt and Grossenheider 1980:208-209).

Woodchuck: Marmota monax Habitat: Open woods, brushy and rocky ravines. Habits: Diurnal for most part, may wander at night in early spring. Feeds on tender succulent plants. Hibernates Oct-Feb. Home range 40-160 acres. Mates in March or April, breeds at 1 year. Young: Bom April-May, 2-6 (Burt and Grossenheider 1980:92).

Eastern Chipmunk: Tamias striatus Habitat: Deciduous forests, brushy areas. Habits: Solitary except for mother and young. Feeds on seeds, bulbs, fruits, nuts, insects, meat, eggs; stores food underground. Hibernates but may come aboveground in middle of winter. Home range usually less than 100 yd across. Populations of 2-4 per acre. Young: 1st litter May, 2-8; 2nd litter Aug- Sep, gestation period 31 days (Burt and Grossenheider 1980:108).

Eastern Gray Squirrel: Sciurus carolinensis Habitat: Hardwood forests with nut trees, river bottoms. Habits: Primarily arboreal, rarely ventures far from trees. Feeds on a variety of nuts, seeds, fungi, fruits, and often the cambium layer beneath the bark in trees; stores nuts and acorns singly in small holes in ground. Nests in

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TABLE 24

Continued

holes in trees or builds leaf nest in branches. Populations of 2-20 per acre. Young: 3-5, gestation period 44 days, 2 litters a year (Burt and Grossenheider 1980117-118).

Eastern Fox Squirrel: Sciurus niger Habitat: Open hardwood woodlots in North and pine forests in South, both with clearings interspersed. Habits: Spends much time on ground foraging, sometimes in open several rods from trees. Feeds on great variety of nuts, acorns, seeds, fungi, bird eggs, and cambium beneath bark of small branches of trees. Nests in cavities in trees or builds twig and leaf nest in crotch or branches, usually 30 ft. or more from ground. Home range 10-40 acres. Populations of 1 per 2 acres. Young: Born Feb-April and Aug -Sep in North, a month earlier in South (Burt and Grossenheider 1980:118-119).

Beaver: Castor canadensis Habitat: Streams and lakes with trees or alders on banks. Habits: Chiefly nocturnal, occasionally seen by day, appears shortly after sundown. Has moved 150 miles or more from birth place, usually under 6 miles. Live up to 11 years in wild. Young: Born April-July (Burt and Grossenheider 1980:151-153).

Mouse (unspecified): Peromyscus sp.

Muskrat: Ondatra zibethica Habitat: Marshes, edges of ponds, lakes, and streams; cattails, rushes, water lilies, open water. Habits: Chiefly aquatic; moves overland, especially in autumn. Feeds on aquatic vegetation, also clams, frogs, and fish on occasion. Builds house in shallow water; also burrows in banks; entrances usually underwater. Young: 2-3 litters a year (Burt and Grossenheider 1980:193-194).

Porcupine: Erethizon dorsatum Habitat: Usually forested areas, but occasionally away from trees if brush is available. Habits: Most active at night, but may be seen during day, especially top of tree, more at home in tree than on ground. Solitary in summer, may be colonial in winter. Young: Born April-May,1 (Burt and Grossenheider 1980:199-200).

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TABLE 24

Continued

Mountain Lion (Cougar, Puma, Panther): Felis concolor Habitat: Rugged mountains, forests, swamps.Habits: Chiefly nocturnal, but may be seen abroad during day. Secretive, seldom seen. Most at home on ground, but climbs trees. Young: May be born any month of year (Burt and Grossenheider 1980:77-78).

Bobcat: Lynxrufus Habitat: Swamps and forests in East. Habits: Mostly nocturnal and solitary. Feeds on small mammals and birds. Young: Born any month, mostly in spring (Burt and Grossenheider 1980:81-82).

Red Fox: Vulpes fulva (also V. vulpes) Habitat: Mixture of forest and open country preferred. Habits: Most active at night, early morning, and late evening; often active during day. Young: Born March or April, depending on latitude (Burt and Grossenheider 1980:72-73).

Gray Fox: Urocyon cinereoargenteus Habitat: Open forests. Habits: Chiefly nocturnal, secretive. Will climb trees to escape enemies. Young: Born April-May (Burt and Grossenheider 1980:75-77).

Longtail Weasel: Mustela frenata Habitat: Not restricted, found in all land habitats near water. Habits: Chiefly nocturnal, but also active by day. Climbs trees, but spends most of time on ground. Young: Born late April or early May (Burt and Grossenheider 1980:58).

Mink: Mustela vison Habitat: Along streams and lakes. Habits: Chiefly nocturnal, solitary except for family groups. Young: Born April or May (Burt and Grossenheider 1980:60).

River Otter: Lutra canadensis Habitat: Along streams and lake borders. Habits: Aquatic but may travel several miles over land to reach another stream or lake. Young: Born April or May (Burt and Grossenheider 1980:60-63).

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TABLE 24

Continued

Striped Skunk: Mephitis mephitis Habitat: Semi-open country, mixed woods, brushland, and open prairie preferred, normally within 2 miles of water. Habits: Chiefly nocturnal, starts hunting shortly after sundown and retires at about sunrise. Young: Born early May (Burt and Grossenheider 1980:65).

Black Bear: Ursus americanus Habitat: In East, primarily forests and swamps. Habits: Primarily nocturnal, but occasionally abroad at midday. Usually solitary, except female with cubs. Eats berries, nuts, tubers, insects and their larvae, small mammals, eggs, honey, carrion, garbage. Semihibernates in winter. Young: Born in winter Dec., Jan. or Feb. (Burt and Grossenheider 1980:46).

Raccoon: Procyon lotor Habitat: Along streams and lake borders near wooded areas or rock cliffs. Habits: Chiefly nocturnal, but occasionally abroad during day. Feeds mostly along streams and lakes. Dens in hollow trees, does not hibernate. Young: Born April or May (Burt and Grossenheider 1980:50-52).

Elk (Wapiti): Cervus canadensis Habitat: Semi-open forest, mountain meadows (in summer), foothills, plains, and valleys. Habits: Most active morning and evenings. Usually seen in groups of 25 or more, both sexes together in winter, old bulls in separate groups during summer. Migrates up mountains, in spring, down in fall. Males shed antlers in Feb-March, velvet shed in Aug. Attains adult dentition at 2.5-3 years. Young: Born May-June (Burt and Grossenheider 1980:215-216).

White-tailed Deer: Odocoileus virginianus Habitat: Forests, swamps, and open brushy areas nearby. Habits: More of a forest mammal. Browser. Occurs in groups up to 25 or more in winter, usually singly or 2-3 (doe and fawns) in summer and fall. Home range rarely more than 1 mile. Young: Usually 2 to adult does (Burt and Grossenheider 1980:218).

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TABLE 25

ODOCOILEUS VIRGINIANUS MANDIBULAR TEETH MEASUREMENTS

(BASED ON SEVERINGHAUS 1948)

306

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 307 + + - - - - + + + - - - - + + + Age 7.5Y 8.5Y 7.5Y 7.5Y 7.5Y 7.5Y 5.5Y 6.5Y 5.5Y 5.5Y B B

3.0 3.86 3.55 7.5Y 2.98 4.45 4.64 3.49 3.61 5.5Y 2.31 4.38 7.5Y 3.15 3.39 4.00 5.5Y - M3/3 M3/P 3.52 3.05 5.21 7.33 6.32 7.85 5.74 7.35 6.5Y 5.75 M3/2 5.96 6.42 4.97 5.67 5.15 4.00 5.17 3.82 4.86 5.12 4.62 7.42 5.69 4.71 5.79 M2/2 M3/1 TABLE TABLE 25 MANDIBULAR TEETH MEASUREMENTS 3.81 4.21 8.02 7.89 7.34 6.76 7.65 1.83 3.45 3.16 7.5Y 4.84 4.14 M1/2 M2/1 (BASED ON SEVERINGHAUS 1948) 4.70 3.70 4.10 4.60 2.44 4.98 3.78 4.17 4.57 5.70 6.32 6.76 4.92 2.85 3.60 5.06 5.33 M1/1 P4 5.11 3.80 6.13 3.83 3.12 3.69 5.10 6.18 6.72 5.53 7.09 4.90 4.97 5.13 6.26 4.40 2.44 3.50 3.27 4.74 4.14 4.32 ODOCOILEUS VIRGINIANUS 5.03 4.23 5.10 4.60 R R Side P2 P3 R L L R L L 4.11 L L R R L 18M 09 18M 09 18M01 18FR18 18M 09 R 18M 09 18M 09 18M 0918M 09 R 18FR18 Site 18M 09 18M 09 18M 09 18FR18 18M 09 18M 04 L

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+ + + + + + 1 i + + 1 1 + 1 + + 1 + S S A > > > > - > > > > - > > - m i n £ i n m in in in m & m m LO i n i n i n t j - •M * M 1' M* M 1 m - M* M" M" x r

QQ

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Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 309

+ + i 1 I + + + + + I 1 1 1 1 1 + 1

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Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 310

+ + i + + 1 1 + 1 1 1 + 1 1 + + + 1 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 2.5Y 20-24M 20-24M 20-24M

c a CQ

0 0 Q. LO

z 6.9 5.16 6.16 6.72 6.52 6.14 5.07 5.96

OO N. NP 5.42 4.87 5.35 6.99 5.31 6.95 6.10

a . z 9.15 9.44 9.77 10.80 10.96 10.60 10.12 10.22 * * 12.18 NP 9.43 9.59 9.26 11.49 11.25 10.01 11.50 10.64

CO 9.06 9.15

o ' 8.59 10.09 10.75 I I 9.55

o CO CO CO 9.15 8.64 9.61 8.59 0 0 7.69 o o ' 7.57 5.91 7.50 6.96 5.92 7.97 5.38 * * 8.54 0 0 CO 7.57 5.99 7.78 6.81 6.56 7.49 c o ' 8.93

CO 0 0 7.73 8.75 7.43 6.40 6.50 7.05 8.30 6.81 6.87 90'S 9S'S 0 0 0 0 CO o 6.58 5.79 6.31 5.54 6.40 CO* 6.76

CO 0 0 CO a> 5.27 4.14 6.56 5.42 4.97 6.56

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Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 25 O —< U T3 c a) c o =j 7 2 2 n z M C M C M C n * s I *• *< O o o o O O O C n O C M C ) O n v o O C — r o L L L L r o c ' O j - O C O C y 1 “ T ▼“ — T f T " M r r f T O C O C n i 0 0 *fr ■ o ) O o v * s I — T O C 0 0 O C * N o cm O C -T- f • a c 2 2 2 2 2 o t . * r * h O C f T O C > o ” T ) O o o “ T ) O o - ^ r O C > o 0 0 ) O n i n i “ T * s I n t ) O > o O C L L L L r . N n i n i cm cm O C D O C C * s I O C > o M C > o 0 0 0 0 O C o o 0 0 0 0 0 0 O C + m ” 7 M C - N 0 0 o n T n n i M C M C T*“ “ T t 7 n o o f “ T Y - 1 V o O C n 2 2 z 0 0 o > o o M* 'M O C O C cm - M O C 0 0 “ T > o + - f T ■M* 7 n . N M C > o - r o c O ( MCO00 0 O C O C CM n O i C O C - M o o o ) O 0 0 * s I CM O C M C “ T ) 0 o o o o iY cm — * 0 0 0 0 i + o o O C - N 2 n i M C 0 0 o “ T * T * O T C > o 2 2 o o 0 0 O —• * o> cm * M O O O C O C 0 0 y < O C M C 2 2 *CO C ) O s* I O C “ T O C > 0 o o mcm cm o o o o 0 0 > o 1 O C o O C 0 0 M C o r* cm L L 0 0 e T 2 2 2 M C . 0 ) O . 0 0 0 * •M 7 o 2 cm ) O f — T M C O C o c o M C — T ) O ) O O C o o f T M- 'M 2 M C O C 0 0 * 1 ^ * M “ T “ T O o o O G o o o o > o ) O + O C M C “ T o — T n i “ T M C > o n i ) O O C ■M* o o o — T L L 2 2 2 O C o o + + * h n i r f T M C M C — T 2 — * 2 o c O C O C O C O C M C l* T * h N ( O C O C o c O C “ T > o k- w * s I * * r n i T™ o o O M C ) O O ” T + > o ) O O C > o > o 2 'M* s* I O C cm 0 0 " T OO + 312

1 1 + + + 1 + 1 + + 1 + 1 + 1 i + +

S S 9M 9M | 9M 7M 5M 3M 6M 6M 5M 5M o o 4M CO 3M 7.5M 7.5M 7.5M 3.5M 10WK

CQ

in ■ o CM (i> D 4.35 LU C —I U —< CQ c o £ o 3.92 6.32 4.89 10.53

CO U i CO 2 8.05 9.12 9.19 6.34 7.49 8.87 c o ' 6.66

CO NE 5.22 9.14 7.68 8.91 8.59 8.07

CO 6.98

CM CM 5.98 4.93 5.35 4.14 4.82 4.65 5.36 5.84 M-' 6.08 5.83 S O S CO CM CO CO S cq 5.96 3.49 4.65 3.41 5.47 4.40 4.50 4.27 3.96 CO CO* CO* CO 4.74 4.50 3.09 3.00 2.98 3.39 3.28 4.47 3.58 3.46 3.67 4.45 2.80 3.68

U.

O) o> o> o O O 2 2 S CO 00 CO 18M 09 18FR18 18M 09 18FR18 18FR18 18M 09 18FR18 18FR18 18M 09 18FR18 18FR18 18M 09 18M 09 18M01 18FR18

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Continued

18FR18 I NE NE 9WK +

18M 09 r 4.57 6.68 8WK +

18M 09 I 3.99 3.42 5.96 8WK +

18FR18 I 3.91 4.21 6.12 8WK +

18M 09 I 3.99 4.58 6.29 NE NE 7WK +

18FR18 r 3.95 4.75 7WK -

18M 09 I 4.08 5.67 7WK +

18M 09 I 4.57 7.07 6WK +

18FR18 r 5.06 5WK +

18FR18 I 4.61 5WK +

NOTES:

1) In the column for S ID E ,' L' and 'R' indicate the presence of permanent premolars and 'I' and Y indicate the presence of deciduous premolars. 2) In the column for AGE, YR=years, M=months, WK=weeks 3) NE=not erupted, NP=not possible to take measurement on tooth that was present due to post-depositional damage 4) B=butchering scars present on mandible 5) + or - =certainty of age assignment APPENDIX FOUR

TABLE 24

BUTCHERING SCAR INVENTORY FOR THE ROSENSTOCK (18FR18)

AND HUGHES (18M01) SITES

314

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. 315 - - 5 17 17 12 13 11 (GRAMS) 11 30 9 6 6 19 2 41 3 19 4 24 3 72 3 7 2 11 22 13 31 14 11 17 # SCARS WEIGHT F M SCAR M TYPE RCp-6 EM-1 M? EM-2 M SCAR# EM-3 M TC-1 M MCd-1 M SPRLB TC-1 TABLE 26 TABLE N/A R PS-7 R R R EM-4 D R TA-2 M R TA-2 M AND HUGHES (18M01) SITES ELEMENTSIDE CALCL RADI CALCL HUMRRSPRLB FEMR METCRFEMR SKAN LLVRT S-4 N/A S EM-5 M ATLS ASTR ASTR R TA-2 M ASTR DEER DEER DEERPELV DEERLVRTN/ADEER DEER DEER DEER DEER DEER DEER ELK DEER DEER BONE TA-1 M DEER BUTCHERING SCAR DATA INVENTORY FOR THE ROSENSTOCK (18FR18) 12 12 12 12 12 12 12 FEATURESPECIES 12 12 5 - 18FR18 18FR18 18FR18 18FR18 12 18FR18 18FR18 18FR18 12 18FR18 12 18FR18 18FR18 SAME BONE 18FR18 SITE 18FR18 18FR18 18FR1818FR18 12 18FR18 SAME 18FR18

Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 O —* U TJ o C 3 0 c

2 F H : a l c uj «? CO Dl o> lO CD < <0 T~ - T oo u 1 LU 111 UJ CL CO LL. a 11 1 2 1 < < CL (O UJ < OCO CO 00 MCM T_ CM a a CL CO CL - M" 2 2 2 »- MC CM CM CM I- CL JU UJ UJ UJ UJ < i— —T 7“ T— T— LCL CL 00 .u.u. u . u U. CL co i T— m 1 < OCO CO < < < < CO h” CL T_ 00 ■*— a JUJ UJ oC OO CO co O' - ”T“ 7” - J h* < C CD -C" <0 LC LCL CL CL CL T— CM r-~ Q CL CL co < CO T- 7— oo co a LC CL CL CL . u . u CL ' CO ■'t CM o o < CO CL 1 MC co CM CM oo nT" in a a CO O' - 316 l _ - J c!> o 5 CM JUJ UJ < < < < < < O - 7 T" MCM CM lU Ul UJ Ul OO Li- CL oco oo i 2 2 CM J-I_i _ I - -J h O CO in a CL t U. CL 7~ OOO CO — CM t— o T— CM a l U o o T“ 7~ oo LC LCL CL CL CL Li- LC CL CL CL 2 CO •M- LU UJ CO o o o O O O H ) ( 7“ —v- 7— CO CM h- D co i U. li. .u. u U. 7“ UJ UJ 1 O O ■M- CO co a T- OO Oin CO CO - 1 _1 H CO CO >r— o> a UJ IU 7“ Li- CL oo OO < < 2 2 CO LU o a CO Q Q UJ LCL CL CO 7 T" in li. CL 00 oo — CM o a a a a CM 7 III UJ OC OCO CO CO CO CO 7” 7“ CM CO . -l.u_ li. U- I.L CL 00 — < CM 2 7 M- III o CO CO T~ Q III CL 7 MCM CM co LC CL CL CL oo — — 2 2 O < CO oO) co Q III III CO t CL 7— 00 co - < 7“ CO o CM D III III CL CO CM 1 7” 0 0 oo ". Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 O " O -< 4 a) o C c u 2 t M C - N dOd Od - T 04 || 18FR18 DEER SCAP S-2 — 2 03 M C o c m M C 18FR18 DEER SCAP 1 2 O C dO dO Od Od Od Od Od || 18FR18 DEER SCAP S-2 2 2 O C M C 18FR18 DEER SCAP S-2 oo M C M C n i 18FR18 DEER HUMR Hd-2 M C n i 2 “ T M C 18FR18 DEER HUMR Hd-2 - r 2 T— Q UJ UJ Od n i 18FR18 HUMR Hd-2 ”T“ T” a 2 dOd Od l T™* O 18FR18 DEER HUMR Hd-3 O C Q C T“ O C . u E O C 317 1 DEER HUMR SPRL 2 2 | 18FR18 SAME BONE Hd-2 1 O C 18FR18 SAME BONE Oblique 1 Hd-2 T— O C T“ S a: M C || 18FR18 DEER HUMR Hd-3 2 O C i _ M C O C T“ M C 18FR18 DEER HUMR Hd-3 m | 18FR18 SAME BONE SPRL 1 > o O C O C j _ i _ n i 18FR18 DEER HUMR Hd-3 T“ O C 0 0 u. E 0 0 SAME BONE SPRL 1 O C 2 2 2 M C M C | 18FR18 DEER HUMR Hd-2 2 8 | | T— O C O C * T 18FR18 DEER ATLS N/A CV-2 O C o Q UJ UJ Od m || 18FR18 ATLS N/A CV-1 Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 O u ■ ■H '■ c C o 3 D C 2 2 n i M C [ [ 18FR18 SAME BONE EM-7 1 CO n i | | 18FR18 1 DEER ATLS N/A EM-7 2 2 2 2 n i > o M C 18FR18 1 DEER ATLS N/A EM-7 * M CO O o i — c < to M C 18FR18 DEER N/A M" ■M M C ~ T M C 18FR18 DEER AXIS N/A CV-5 M C - T O C M C 18FR18 DEER AXIS N/A CV-5 2 2 2 s “ T CO O C _i “ T M C 18FR18 BEAR ULNA RCp-4 > o M C M C OH CO in 18FR18 DEER ULNA RCp-5 - T OH M C || 18FR18 DEER ULNA RCp-2 318 “ T I — M C ” T 0 0 I. L O' O C DEER ULNA RCp-3 . u ) O W UJ Ul OH OH Q 18FR18 RADI RCp-6 2 o c M C o i _ 18FR18 1 DEER RADI RCp-5 n i 3u u. u_ 03 J _ M C 18FR18 DEER RADI SPRL n i UJ 2 O C h o “ T CM [ 18FR18 DEER RIB ■ “ T 2 Ul O C M C 18FR18 DEER RIB 1 2 i CO n i HOH OH 18FR18 DEER RIB RS-3 IJU ’ M " T O O m 18FR18 DEER RIB EM-8 u. CO M C j - M C 18FR18 DEER RIB EM-8 - I L “ T f T LU 2 OO J - M C 18FR18 DEER RIB i L U “ T m O C Ul UJ OH OH m Q || 18FR18 RIB EM-8 Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 o < - 4 T3 o (U c c o M C Ooo o lO 3 2 . u U L — ^ — ^ n o Q C - T - T o o L L n o Q U L n J o U n U o L J U n o o o 1 1 2 M C M C h 5 n o L I n o J U U L - h o o o c Q C Q C Q C Q C Q 3 0 u 3 0 u o M ( o o T— “ T p 2 - V L— - » o c n o 00 i. L 0 0 ■ n o i _ i H L C m n o n o “ T 2 2 2 < 2 J U 2 J U T— 00 LL o o m o 1 D I T L L M C O C l _ - L 3 T - T Q C —T“ T T— L L “ T J U M C J U n o 00 O O l _ 1 _ l _ J - T— L C n o Q C i H J U l U J U Z l U OCO CO LL n o 0 0 0 0 i H o < t M C O C L L L L O C - 1 0 " T - i 5 n o n o —T“■—^— ^ ■t— “ T T— l U J U n c “ T L L L L M" ■M M C o o - - I L L 1 > L L J U 2 n o n o - T n o l U M C < o o O C M C o o >-OCO C O - l> L L 2 2 J U T— L L n o n o n o o o ) I t « i H < Z 00 . i . i 319 2 n o n o n o n o L L L L . U > • L L l U L U J U ) U r < o o o o M C 0 0 L L L L Z l U L L O T_ 00 O C i H 4. 1 3 T T o c M C U L 2 n o . U l U n o J U n o “ T o o L L n o O O M" ■M v J U J U M C M C M C Q — T ) O L L 2 L L J U 2 n o n o OO L L n o Q O C 4 . n o — * L U l U 2 o c L C Q C ) - - i n c in u L L L L L L n o “ T n i n i — T OO o o ) O J T o c O C 2 — i 5 n o - 1 n o J U l U J U o Q J U n o 00 o o i o n o h h - | O C 2 2 J U - r 1 _ 3 1 i H . Q Q C n o lO J U n o ” T o o o o — t o o — ^ n o J U - r i H L C - ^ C Q C * T “ T l U a J U n o - T 00 n o o c ■» !■ M C — ^ J _ D > z l U 2 2 J U - 1 l U J C n o ” T o o _ u n o o o i M C “ T M C - r - 1 i H L C n o Q C l U n o l U l U 2 L L n o n i Q “ T 00 o o 2 o T— - "M M" "M H l U 2 D I U L n o Q l U o . I L n o 0 0 M C o o 1 Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 O 3 T o c C 3 (1> > > > UJ > a a a nCM in lU lLU Ul UJ Ul u UJ T— co oOO co LL a: T“ 2 in f- (O _l .a a. UJ _l Q Oo OCO CO oo CO ^— f LL UJ T— a - T” O2 CO a 2 2 w UJ _j _i in T“ a D JUJ UJ T“ a: CO T™ Mc ■M- co CM co UJ _i a a a a w a a T— a co a Q a CM a a in o w *? Js UJ _j UJ in v T— T“ CO >!> :> T CO 05 2 a a CO CO T“ UJ Ul UJ Ul a a UJ a T— T_ oo oo CM a T“ CO CO co x; 2 f- < t r" Oco CO CMCM a □ UJ a a CO a — CO > a H 2 2 2 a 2 2 F* T“ a a Q UJa UJ Ul *«— T“ 0CO 00 a a Om (O J> F F f- > F a H T“ 320 T“ MC MCM CM CM CM a a T“ CO x— in f > a F- CM in lU lUl Ul UJ Ul a a Q a T_ CO co co a a m 2 T" ■> a 2 UJ UJ UJ 2 T- ^— *T“ T* >i $ T- CO LU a r" Min CM > a _i 2 2 2 CM 2 —T T“ T“ ^— a T_ 00 t— 00 UJ Ul Q a a a CM a F F > a <: 2 2 T- Li QQo Q CQ a T— o0 co 00 co oo U. a a CO a £ )L1J C) 111 UJ w 00 < 5 a: U) 0) in CO CO 2 > a ia_i a _i 2 2 *— _i Ul 2 2 Ja UJ i 1!. li. a a a a a T- co CM CM CM a a a a <. ^— CO in 2 *> a _i Ul UJ T™ co oc o00 oo co oo T— D 2 X a M- O' CD ii III in ~i 2 CO a r— a F 0O 00 OO 00 MCMCM 2 CO F- LL a a a a a DCDCD Ja UJ a co -T T— T“ v- f Q Q Q a T” - 2 2 L in LLl a a oOO co -t- T“ F- 3 T“ CD CM a in LL 00 V 00 r r 321

C M i n T t CMCOCO T- o O) 1 CO o o (O CON. (OM" i n c o y — CM x — T“ T- CM ^ — CM CM CMCM Y“* Y“ Tt“ c o

C O T t ■M - CM CM i n c o CO M 1 c o o » CM CO o T t CM CO T-

LL l l LL 2 2 2 u . l l l l 2 LL LL 2 LL 2 2 2 LLU. 2

lO i n t o c > - CM CM t— T- CO Y™ < 0 CMCM 'T 9 i . i . d i. i . I > i CM CO 6 . * o P O O OO A. 2 C ) o 2 O O < f < r < f h - X H i l U 1 ft I t LL UJ t - J— UJ t - H- v - H COCO CO

tt _ j a : —I tt _J O' _ j - 1 tt tt tt tt _ J _ 1 ft

or < tt o o o O O tr tr tr CL CLCL T* u u u 7 -J - 1 _ J _ l < < < -J < U l < < < < <

01 01 tt tt O' (t tt > ft ft UJ a: tt ft tt ft tr tr. i r * tr LU UJUJ UJUJUJUJ < UJUJ Z UJ UJUJ 11.1 U l i n h i i n i n UJUJUJ UJUJUJUJ U l UJUJ o UJUJUJ UJ UJ in in in in Q UO a u a G m a Q m a Q a a Q a a a a

UJ 2 r- r«- N. h- N. l>- h- CM < CMCMCM CM CM Y“— ^ T“ T— t— t— T“ t o Y-* UJ in T* i n i n T* T“ i n

OO o o o o CO CO CO o o o o o o OOCOCO 00 o o o o 0 0 o o c o CO o o r- V" ■t— T“ Y“ T— Y— T* t— T— a: 01 tt tt tt tt tt ft tt tt ft ft tt ft tr. ft tr tr tr tr LL LL LL u. LL l l i l l l u. u. LL u . LL l l ii. U. i i i i . i i LL 00 00 CO 00 o o 00 o o o o o o c o 00 CO 00 o o 00 o o CO CO 00 00 T“ Y— T“ 'r— T“ T— Y“ T* T“ Y~ Y“ T— T— Y“ r_ T_ T“

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TABLE 26 •o o o c C 3 0) O C L U M C M C I I I < j u 2 CDC . u DC “ T o O m o c O C T” o o JCL C .J r I 1 2 DC co M- •M o c X O C O < . Q U L DC U L O C O C 0 0 O C u_ " T o o DC Q C J - 1 - O C J - M C > o — T ) _ 2 i Q U L DC U L M C Q C D C Q o o 0 0 L L DC - T OO X o • 2 2 O C * 1 * M C O U L U L o < J U < J U 2 2 T“ i- L O' OO X O o - M C Q C □ G J U “ T a “ T ~ T X o o o T™ 00 L L DC 1 X J T L C > T 2 . N L L X X M C * } * M C 0 0 J U J U > _ > _ 2 DC J U r t u O C G u n i O C O C o o o c - T — Y L I DC 00 Q C DC L L X O C DC J _ T— M C M C 2 DC J U DC M C O O 000 00 L I DC ~ T 2 2 M C M C O C X J U 2 2 o c o < J U CO L L . U DC . U DC — T 322 J - D " M C 0 0 O C I I I 2 DC l U nr l U T— 0 0 — T 00 L U 1 - L L u 2 I I I 2 DC D C O C J U nr J U J U Q “ T — T o c 000 00 “ T 0 0 o c DC X L L 2 DC DC O C . Q DC J _ Q C m — ^ - T J U ' r r I I I Q C Q n i - LL T L L o c DC 2 L L t— 't X l U o l U l U < l U O C T— T— o o CDC DC 1 2 " •M < G Q J _ DC o n i n i O C l U DC J U Q C Q Q C Q > u T*“ o o t O C LL L — O C O C . n . n DC Q C Q C " T X l U J - o < O C m O C < 2 T— o c o c L L DC o o o o o o 1 r < DC DC C < i _ DC n i nr J U J _ O C “ T LL V CDC DC 2 M DC O n i X l U o 2 2 7— “ T CO L — T . 6 l 1 1 — . u O O DC o O C M C O C I I I n i nr U L l U o 1 M C M C o o o o 0 0 i i : r i . 2 DC l _ DC O O - r " •M DC G O C CO'. O . I I DC . i n i L L l U DC X o m n i £ O C < OO o o i- L 1 Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 O TJ C o C D CD CO | 18FR18 SAME BONE SPRL 1 ’M’ o V 3 0 a a J U j u cm m c

18FR18 RADI : SPRL CM L L J - 18FR18 SAME BONE 1 1 s 5 18FR18 SAME BONE RCp-5 2 CO cm lO 18FR18 DEER RADI RCp-5 o> • 2 cm lO m

18FR18 DEER RADI RCp-5 - s CO J - L U O C CM O C DEER ULNA RCp-2 L I CO £ “ T o o L L 00 SAME BONE RCp-7 i L L ▼— CM (0 cm n i

18FR18 DEER RIB EM-8 323 3 cm O C LL co IO II 18FR18 DEER RIB I “ T “ t T T OQ i _ Q l U U L cm CM || 18FR18 TIBI SPRL L L 18FR18 SAME BONE Td-4 1 5 2 MCO CM CO cm CM [ 18FR18 DEER TIBI Td-1 IO CM - v CM || 18FR18 DEER SKLL N/A S-1 CM 2 * T M C [ 18FR18 DEER MAND M-4 2 2 O C CO cm n i 18FR18 DEER MAND M-4 CM o> w “ T * N 18FR18 DEER SCAP o i i L D D 2 O C m 18FR18 DEER 1PHL 1 l U T“ Mh- CM CO 2 O C CM 18FR18 DEER 1PHL 1 L L a: t n i CO CO

* ELK FEMR Fd-2 209 Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 •o o o c C 3 CD Oc CO co CO LCL CL CQ lcl cl _] T— — t — ^ . u UJ m o o 1 0 < > 2 o UJ z CO Oin CO 1 T— _J -H 1- Q C CL CQ o CO _l Z IL — * UJ O00 OO O' 00 r- Q C cl CL CQ O' T” l-J _l Z Z il -1 l i JU JU JUJ UJ UJ UJ Ui UJ MCM CM o o < •*r 0<<<< < < < < <0 _i h- 2 CD T— DC 00 L I O' OCO CO 1 CO CL aC QCQ CQ CQ ca in n £ a CL CL _i . u T* o o CL. in _i z a —I OC CO CO CO CL o> CL . . L L CL — y _i z 00 00 1 _J CL r-~ 1^- CL a Q CL L L L L —T“ T— Z .1 OO CL o o in _l il CL CL 00 03 T“ CL _i z CL . . 00 Mo CM 00 1 ^ il < 5 J OCO CO CL QCQ CQ 03 — i L L L L CL T— J U _1 Z Z CL 1. C^ .1 .1 00 o o T— 324 — X D 2 CL CL O CM “ T OO CL — ^ in UJ _l O' CL o o CL ± 2 ■M" T— L L T" Ul CL < 2 Z ■a O0 00 00 CO 00 / nin in C/J Q C o UJ 1 T” 3 y < CL O 2 o o lU UJ Ul Ul -T"“ T- l i CL _J Z V 00 a. _i CM X D 2 CO CL J_j _J CD CM CO . u . u : a —1 CL il o o < Z 2 CD 2 Q CL o o o o CL t _i z T OOO CO — T“ . Q Ml CL CL CO 2 00 i i li. li. li. £ Q U L J - CM V ON* CO Q- OCO CO CM LCL CL Q C o UJ t CO < 5 z o o 00 Ul — i CL o CL III >1 CL h- 2 CO (O o o ▼" in Ul I — V o o 2 T“ in in lUl Ul £ _i CO n CQ i. L L I r r in UJ I — V IT " T O0 CO 00 CO 00 2 T“" 2 < UJ 2 U CO O■n CO Q C ) ( T_ n z U L o o CL 1 J- _i CO n 2 o CL _J CD CM t i. L f UJ _l V 00 — Y Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 O U-* ■o C o c 13 D ( i - Od CO CL rt m I- O J—I _J III T— " T 0 0 L L Od nin in UJ V “ T CO 1 Q. or I - m (O (O o o >_i z> CO JL CO LU UJ s UJ OCO CO LL dOd Od V CO F- “ 't in O CO CQ CL tr -1 UJ L L _l V co CO — IT) T“ 2 2 5 u T— l i Od UJ co — T (0 < _l u z UJ co CL 1 1 T— CM CM 3 3 3 CO CO CL rtr tr _l F* O JU UJ UJ UJ —T“ T— . u L L L L : a JUJ UJ V V V 2 2 2 0 0 " t oo 1 •M- CM CO OCO CO CO a. . ...1 -.1 -F- r- t 0 0 Od T“ in 00 T— CO T— CL tr CO t UJ —1 T“ oo a: T“ CM CO co CO tr CO n 3 CO CL _l < T- L L Od t in Jca UJ —I V od 0 0 CO — Od o in 2 co L I Od CO < 2 Ul UJ oo CO IJ A. ck 325 1 •M- CM F- o

1 262 7 Od u- y *— 0 0 Od T™ Od 218 Q) CO CM 7 _i OCO CO T OCO CO y T_ IL Od ni in a lUJ Ul :a: a: OC CO CO CO oo - Y OOO CO CM o o> 7 Y“ _i T y L L 0 0 Od Q •V *d 7 a c CO a >y v> T— L I Od ^ MCM CM LU dOd Od oo Y“ CO — 193 Y“ CM o T— i li li. dO Od Od Od 7 Od CO a CO _T_ T_ oo in II.J UJ CO CO in in Od O 2 r- n l_i _l 2 2

TABLE 26 o ■o o c C 3 0) O) o U. Z r>- u. u. —T“ T— _J O CD . u . u dO dO dOd Od Od od Od Od < 2 “ T CO T— 1 3 3 3 3 3 UL 3 Z o 3 < 2 CD T- t oco oo — 1 I co O) .LL u. 2 2 2 3 oo UJ lU lUJ Ul Ul Ul u Od > ll UJ UJ T“ co CM nin in Z 3 3 3 3 3 2 2 2 O DC CD CD CD 00 U. 0oo 00 2 < 1 CM u_ h- —i T— Z o Z . u 2 < t 00 T- — I CM .u .u _L IL LL U_ u_ u. u. u. 2 o o 3 o T“ LL T- 2 2 2 < 2 < 00 oo — i I co >'S- o> 3 3 c- 2 UJ 2 T— 1 - 3 Z Z Z Z DCD CD " T . u Od 2 oo oo — 326 CM T* 3 h- lUJ Ul 3 < 2 T— 00 . u Od o00 oo I * V CO 3 2 3 3 o i-~ U- dOd Od 3 2 2 2 < 2 < 2 CD T_ o00 oo 1 1 CM 1^ 3 3 3 3 3 2 3 3 3 o Ul 1". N- h- t . u DC DC CD CD CD CD CD —T“ T— CO — CM CM Z Z r* 2 2 o 3 o < < < < JUJ UJ 2 U. Od CO ooo oo i ■M- 3 2 u. Od —T- T— T— oo I MClCM Csl CM u. Ul 2 3 3 3 o T“ Z ^— . u 2 2 2 2 2 ~ T CO £ CO 1 LL. ID lU JU Ul UJ UJ Ul Ul Z Z Z r^- Is*. 2 T“ 3 3 3 3 o 2 2 L11. LL dOd Od T_ 00 oo I IL 2 3 o 3 3 T— < DCD CD T" CM " T o0 0oo 00 00 oo oo T— IL 2 2 co 3 o o 2 CM _ r ' < U. Od CM T- 0oo 00 m LL ^— 3 2 2 Z 3 T“ T_ N < CD .u. u. Od t T— — U- N- CM 3 3 o Z f>- 3 r— 2 CM 2 < CD r r r T“ CO T“" Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 o ■o C. o c a) 3 — T Z l l o c o c - c 2 2 2 3 o 3 D C 3 3 J U J U J - 2 2 < 2 2 2 i _ 2 i — 2 T_ M C O O “ T o o T- o 0 o 0 1— £ O C o o l l £ o o . L L L U o c - 1 2 - T " T O O O D C J — < < l l ■ o o - " t Z O C D C D C l U J U 1 - O I l _ £ L L t 0 0 — O I - f Z “ T L L 2 2 2 i _ . < 5 £ “ T . u ” T — T M C T_ o o L L O I o c 2 2 2 2 2 2 3 2 3 3 3 1 _ J I - I - I - D C J U l U l U U L O ( O **” 5 2 s 2 < 2 < 2 < 2 M C j _ j _ £ 0 0 0 0 0 0 0 0 0 0 L L L L L L L L M C - h " T D C D C O D C ? . M C - r " T - r 2 2 £ £ o o ” T T— . u T— M C - - r-~ IO — ^ O o o t L L — - f ^ 1 . T— N O C 2 O < < < < < < < M C ~ T < M C < < i — < £ £ £ 0 0 £ o o " “ T L L “ T 3 3 3 3 L L L L “ T D C J U D C l D U C J U J U J 2 U J U 2 J U 2 O O O M C M C - T - T 1 - L L L L L L 327 M C J - 1 - — T i _ O I o o T— 0 0 o c “ T M C . N L T— - v o c o o t OO O O l — i ~ T o c D ( D C D C 2 D C D C 2 D C 2 D C 2 D C s 2 2 ^ 1 O O j _ L L £ £ £ £ i — T— L L i 3 i _ L L “ T “ T - h . * h o o 1 - M C M C " T 0 0 o o O O O C o o T_ L L O I 3 L L o o 1 - J - 2 * r T— l l O I l _ M C 3 L L * - o o “ T L L 1 2 2 2 3 3 O J _ i _ o - T 2 2 2 2 O C . a l U l U J U L £ £ £ £ £ o c j _ _T_ T_ L I O I O I o o 0 0 0 0 0 0 l o O I “ T L L “ T “ T - l» O C ? ? O O l _ J L i _ 2 o o o o o c o o l i l _ J _ 3 “ T - ' ' I L L M-■ - ■M - ■M T_ L I O C i _ L L 9 < l U l U £ “ T l l M C 2 3 M C T— . " I 2 J U O L L < O O T- L L ■ 328

i n 0 5 CM 0 5 CO CM c o T— i n CM CO c o CM T— CM T“

0 0 T“T" CM CM ^ — CMCM CM CM o o T“ i n i n C O C O h -

LI-CDCQ c a c a c a m c a c a c a c a LL c a u . 2 2 2 L L LL LL

O O o > G i 0 5 0 5 0 5 C D 0 5 0 5 0 5 0 5 i n i n i n T“T“ t — CO ■ *p i p ▼ p C O r y o o A. i . 0 0 0 0 2 2 2 2 2 2 2 2 2 2 2 2 a . 2 o O O 2 2 2 H i U J U J U l U J U J U J U l U J U J UJUJ CO U l on on on LUUJ U l

3 3 3 3 3 3 3 3 3 3 3 3 3 3 on _ i on 3 3 3

o O 0 0 0 0 0 0 0 ( 9 P z z Z Z z Z z z Z Z J- a C l a c a CD c a c a O o o o o o o O o o UJ < < < U l _ 1 - J - J - 1 _J _ J _ l -J-I on 2 on £ £ t E on on on

on 2 2 2 2 2 2 2 2 2 on on on on on on or, or. or. UJ < < < < < < < < < UJUJ U l L U U l L U UJ U l U J UJ 2 2 2 2 2 2 2 2 U l U J U l U J U l L U UJ U l U J u _ i _ i _ i _ i - j - 1 — i _ i o u o u o a a Q u

CM CMCM CMCM CMCM CM T“T— i n T— T” T- T“ T“ 1 i n ■ ■ ■ * " ■ T— ■ ■M - i i n 1

c o 0 0 0 0 c o c o o o o o c o CO 0 0 c o c o o o o o o o o o c o o o c o 0 0 T— T- T— T- Y“ T“ v r - t — on a : on on on on on on on on on on on on on on on on on on i l LL. L I - L i­ L L l l L i- L i- L i- l l LL u . LL LL LLLL u. n . i i . LL CO CO OO a s CO c o OOOOOO c o C O o o o o CO o o CO o o CO 0 0 CO T_ T“* T” i— ^— T— ^— T ™ T — T" T- T— T— T— 'T“ T-T-T—

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ZZ CL oz m — T oz O C i _ 18M01 DEER RADI T— w iJ L 2 i. L - h V lO 18M01 SAME BONE 1 _ u 2 M C 1 —

18M01 22 DEER PELV PS-7 0 0 n i ZZ T*“ o n i 18M01 DEER TIBI OZ EM-26 “ T 3 0 “T“ T T“ i - I 18M01 22 DEER TIBI SPRL O C 2 2 O C < 2 l i t 18M01 BONE Td-3 1 T“* 18M01 22 DEER CALC FL o c M C M C OZ T— || 18M01 M C M C DEER ASTR TA-1 t D 2 O C — 18M01 22 DEER 1PHL EM-27 330 M C i. L D o U L 2 M C M C 18M01 ELK FEMR 1 D C M C

18M01 SAME BONE EM-19 ■ ZZ CD T— T"" o D “ T GO 2 O DEER METP SPRL OZ 2 o

18M01 M C M C DEER C4TR TNC-1 ZZ T— I _ O C L C OZ m t j _ 18M01 DEER TIBI —

18M01 SAME BONE EM-17 1 2 T ZOZ OZ i H 2 M C o c O C 18M01 45 BEAV TIBI — M C CL 2 n i O C J U 5 18M01 n i BEAV PS-7 D . a 18M01 LMAM LONG EM-17 M C O C D L L T— M C 2 o co LMAM LONG EM-17 D L 1 M C 18M01 LMAM LONG EM-17 ' Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. without prohibited reproduction Further owner. copyright the of permission with Reproduced

TABLE 26 O —< U _C 3 T o c

3 2 - T -. h . u —I Z CD UJ O ■M- 2 2 2 2 T_ 00 2 o U 3 < 2 1 CO 2 tf ft ft ft ft CO to ft Om GO T_ UJ l U l U oo A _U. U U_ MCM CM 3 3 UJ 2 2 oo 0 ( GQ o o o OCO CO i - Z CD l U - N n T“ - T * r j - t f t f t f < 2 331 r < 3 2 CM 3 z ft ft O co a a a oo UJ A GQ 3 3 3 t f - U CO UJ 2 oT— co o o o UJ UJ 111 I IL 2 2 oo 2 NG 3 ■M- t CD CD x— CO _ CD “ T 0oo 00 | 3 . U * N CO o Z CD UJ 2 * - * 2 3 s < BIBLIOGRAPHY

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