Arianne Boileau M.A. Thesis 2013 Maya Exploitation of Animal
Transcription
Arianne Boileau M.A. Thesis 2013 Maya Exploitation of Animal
MAYA EXPLOITATION OF ANIMAL RESOURCES DURING THE MIDDLE PRECLASSIC PERIOD: AN ARCHEOZOOLOGICAL ANALYSIS FROM PACBITUN, BELIZE A Thesis Submitted to the Committee of Graduate Studies in Partial Fulfillment of the Requirements for the Degree of Master of Arts in the Faculty of Arts and Science TRENT UNIVERSITY Peterborough, Ontario, Canada (c) Copyright by Arianne Boileau 2013 Anthropology Graduate M.A. Program January 2014 ABSTRACT Maya Exploitation of Animal Resources during the Middle Preclassic Period: An Archaeozoological Analysis from Pacbitun, Belize Arianne Boileau This study examines the foraging strategies of animal resource exploitation during the Middle Preclassic period (900–300 BC) at the ancient Maya site of Pacbitun, Belize. The faunal remains analyzed in this study were recovered from various domestic structures associated with the production of shell artifacts. Detailed taphonomic analyses have revealed that the Pacbitun faunal remains were particularly affected by weathering and density-mediated attrition. White-tailed deer was the prey most frequently acquired by the Middle Preclassic Maya of Pacbitun, followed by other lower-ranked artiodactyls. A variety of less profitable prey were sometimes included in the diet breadth. Using the central place forager prey choice model as a framework, the analysis of diet breadth, habitat use, and carcass transport patterns suggests that most animal resources were acquired from terrestrial habitats, at short distances from the site. Complete carcasses of large game appear to have been frequently transported to the site, where they were exploited for their meat and marrow. Comparisons with other Middle Preclassic faunal assemblages indicate significant differences in terms of taxonomic composition, with an emphasis on the procurement of fish and turtles. It is suggested that the Middle Preclassic Maya adopted foraging strategies focusing on the exploitation of local habitats, with occasional use of exotic resources. Keywords: Archaeozoology, subsistence, foraging theory, animal resource exploitation, taphonomy, ancient Maya, Middle Preclassic, Pacbitun, Belize. ii ACKNOWLEDGEMENTS The completion of this thesis would not have been possible without the support of many individuals. First and foremost, I would like to thank my advisor Dr. Eugène Morin, who showed support and endless patience every step of the way. His edits and advice have helped me to become a better writer and researcher. I am deeply thankful for all the time and effort he invested in teaching me and cannot thank him enough for the opportunities he has granted me. I would also like to express my gratitude to Dr. Paul Healy, who kindly shared his love of Maya archaeology with me. His help, advice, and encouragements are deeply appreciated. I am indebted to Dr. Terry Powis for inviting me to join the Pacbitun Regional Archaeological Project (PRAP) and allowing me to examine the faunal material from Pacbitun. He certainly deserves special mention for answering an immeasurable number of emails concerning the excavations at Pacbitun. I also wish to thank Dr. Carolyn Freiwald who graciously accepted to serve as my external examiner. Comments and suggestions provided by all the members of my committee contributed to improve this thesis. I would like to thank the Institute of Archaeology (IOA) in Belize, especially Drs. Jaime Awe and John Morris, for granting permission to export the faunal material analyzed in this study to Canada. My gratitude also goes to the staff of the Department of Vertebrate Paleontology at the Royal Ontario Museum, particularly Dr. Kevin Seymour and Brian Iwama, for their warm welcome and for providing access to the ROM vertebrate comparative collections. Further thanks go to fellow Maya archaeozoologists, Norbert Stanchly and Dr. Erin Thornton, who provided useful information on the identification of vertebrate remains from tropical environments. I also greatly appreciated iii and learned much from my discussions with them. I extend my gratitude to Dr. Jocelyn Williams for her assistance in the identification of human remains. I am deeply grateful to Dr. Gyles Iannone for inviting me to participate in the Social Archaeology Research Program (SARP) in Belize and for allowing me to collect animal specimens that are now part of the archaeozoological reference collection at Trent University. Gyles provided me with my first opportunity to excavate at a Maya site and trusted me in the supervision of an excavation unit, which I am thankful for. This first trip to Belize made me discover an incredible country filled with history and beautiful people. I never looked back at my decision to study Maya archaeology from that moment. This project would not have been possible without the financial support from a number of sources. My research was funded by a Joseph-Armand Bombardier Canada Graduate Scholarship from the Social Science and Humanities Research Council (SSHRC) and a Fond de Recherche Société et Culture du Québec Master’s scholarship. I also wish to acknowledge the financial support of Trent University which allowed me to complete the present study. Thanks also go to my fellow anthropology graduate students. In particular, I am grateful to Shannen Stronge and Esther Beauregard for reading over and editing my chapters. I also would like to thank all the people who, over the course of the past three years, have become both friends and colleagues: Steven “Morgan” Moodie, Esther Beauregard, Kendall Hills, Shannen Stronge, Jodi Schmidt, Kat Elaschuk, Amandah Van Merlin, Dan Savage, Véronique Belisle, Hannah Schmidt, and Kristine Williams. Their support, help, and humour have made my stay in Peterborough an unforgettable experience! I also wish to thank them all for answering an endless flow of questions about proper English grammar and syntax. iv Last, but not least, I would like to thank my family. Merci à vous tous pour votre amour, vos encouragements et votre support, car sans eux, je n’aurais pu surmonter toutes les épreuves qui ont entravé mon chemin. Maman et Papa, je vous remercie de n’avoir jamais questionné mon désir de devenir archéologue et pour toujours m’avoir poussée à réaliser mes rêves. Cela a fait toute la différence. Philippe, merci d’être le frère dont j’ai besoin et de nourrir mes heures de travail de bonnes suggestions de musique. Grand-maman, merci de toujours me poser les questions les plus pertinentes concernant mes recherches et de m’avoir incluse dans tes prières. v TABLE OF CONTENTS Abstract .............................................................................................................................. ii Acknowledgements .......................................................................................................... iii Table of Contents ..............................................................................................................vi List of Figures ....................................................................................................................ix List of Tables ...................................................................................................................... x CHAPTER 1 : Introduction .............................................................................................. 1 1.1 Research objectives .................................................................................................... 2 1.2 The setting .................................................................................................................. 3 1.3 The Middle Preclassic period ..................................................................................... 5 1.4 Thesis overview ......................................................................................................... 8 CHAPTER 2 : Middle Preclassic Maya Diet ................................................................... 9 2.1 History of Maya archaeozoology ............................................................................... 9 2.2 Ancient Maya diet .................................................................................................... 11 2.2.1 Plant remains .................................................................................................... 11 2.2.2 Animal resources .............................................................................................. 14 2.2.3 Middle Preclassic use of animals ..................................................................... 22 2.2.4 Stable isotope analysis ...................................................................................... 27 2.3 Summary .................................................................................................................. 29 CHAPTER 3 : Site Description and Previous Research .............................................. 30 3.1 Geographical context ............................................................................................... 30 3.2 Archaeological investigations .................................................................................. 35 3.3 Site chronology ........................................................................................................ 38 3.4 Middle Preclassic investigations .............................................................................. 41 3.5 Artifactual assemblages from the Middle Preclassic period .................................... 46 3.6 Subsistence practices ............................................................................................... 48 3.7 The Middle Preclassic at Pacbitun: A summary ...................................................... 51 CHAPTER 4 : Foraging Theory ..................................................................................... 53 4.1 Theoretical approach ................................................................................................ 53 vi 4.1.1 Prey choice model ............................................................................................. 54 4.1.2 Patch choice models ......................................................................................... 55 4.1.3 Central place forager prey choice model ......................................................... 57 4.2 Archaeological applications of foraging theory ....................................................... 59 4.2.1 Use of foraging models in this study ................................................................. 59 4.2.2 Prey rankings .................................................................................................... 60 4.2.3 Abundance indices ............................................................................................ 64 4.3 Animal ecology and behavior .................................................................................. 65 CHAPTER 5 : Methodology ........................................................................................... 75 5.1 Definitions and identification procedures ................................................................ 75 5.2 Quantification methods ............................................................................................ 76 5.2.1 Strengths and weaknesses of NISP, MNE, and MNI ......................................... 78 5.2.2 Use of quantification methods in this study ...................................................... 81 5.3 Refitting ................................................................................................................... 82 5.4 Age and sex .............................................................................................................. 83 5.5 Taphonomic modifications ...................................................................................... 85 5.5.1 Fractures ........................................................................................................... 85 5.5.2 Butchery and tool use........................................................................................ 86 5.5.3 Carnivore ravaging ........................................................................................... 88 5.5.4 Fragmentation................................................................................................... 90 5.5.5 Burning ............................................................................................................. 91 5.5.6 Additional taphonomic agents .......................................................................... 92 5.6 Summary .................................................................................................................. 94 CHAPTER 6 : Sample Description and Taphonomy ................................................... 95 6.1 The Pacbitun faunal assemblages ............................................................................ 95 6.2 Taphonomy .............................................................................................................. 99 6.2.1 Testing the stratigraphic sequence ................................................................. 100 6.2.2 Recovery methods ........................................................................................... 102 6.2.3 Density-mediated attrition .............................................................................. 104 6.2.4 Bone burning ................................................................................................... 108 6.2.5 Post-depositional destruction ......................................................................... 109 6.2.6 Bone surface preservation .............................................................................. 111 6.2.7 Human and carnivore agents .......................................................................... 114 vii 6.2.8 Taphonomy of fish and birds........................................................................... 119 6.3 Summary ................................................................................................................ 121 CHAPTER 7 : Results ................................................................................................... 123 7.1 Taxonomic composition......................................................................................... 123 7.2 Skeletal part representation .................................................................................... 125 7.3 Mortality profiles ................................................................................................... 129 7.4 Scheduling of activities .......................................................................................... 133 7.5 Diet breadth ............................................................................................................ 133 7.6 Habitat use ............................................................................................................. 139 7.7 Transport selectivity............................................................................................... 142 7.8 Processing of skeletal parts .................................................................................... 147 7.9 Pacbitun foraging strategies: A discussion ............................................................ 149 7.10 Subsistence strategies in the southern Maya lowlands ........................................ 152 CHAPTER 8 : Conclusion............................................................................................. 160 8.1 Research summary ................................................................................................. 160 8.2 Limitations and significance .................................................................................. 162 8.3 Future Directions ................................................................................................... 163 Bibliography ................................................................................................................... 165 Appendix A ..................................................................................................................... 200 viii LIST OF FIGURES Figure 1.1 Map of the Maya subarea including sites discussed in the present study. .........4 Figure 3.1 Map of the Belize Valley .................................................................................31 Figure 3.2 Location of Pacbitun in the Upper Belize Valley ............................................32 Figure 3.3 Map of the Pacbitun settlement survey............................................................34 Figure 3.4 Plan of the epicenter of Pacbitun. ....................................................................35 Figure 3.5 Core zone of Pacbitun......................................................................................36 Figure 3.6 Chronology and ceramic complexes of Pacbitun in comparison to those of Barton Ramie, Xunantunich, and Cahal Pech. ...................................................................39 Figure 3.7 Plan of the Middle Preclassic sub-structures in Plaza B..................................43 Figure 3.8 Plan of the Middle Preclassic Sub-Structure A-1 in Plaza A. .........................45 Figure 4.1 Ranking of mammals at Pacbitun according to body mass .............................63 Figure 6.1 Fragment size distribution by screen size for all faunal specimens in the Pacbitun Middle Preclassic assemblages. ........................................................................103 Figure 6.2 %NNISP of long bone portions of white-tailed deer versus bone density values (g/cm3) ..................................................................................................................107 Figure 6.3 %MAU of long bone portions of white-tailed deer versus bone density values (g/cm3)..............................................................................................................................107 Figure 6.4 Gnaw and cut marks on the distal end of a right white-tailed deer femur .....118 Figure 7.1 White-tailed deer body part representation in the Middle Preclassic assemblages at Pacbitun ...................................................................................................126 Figure 7.2 Comparison of white-tailed deer element frequencies (%NNISP) in the Pacbitun assemblages with the reindeer MUI, grease index, and UMI. ..........................145 ix LIST OF TABLES Table 2.1 Plant remains recovered from Middle Preclassic deposits at southern lowland Maya sites. .........................................................................................................................12 Table 2.2 List of identified taxa recovered from Middle Preclassic deposits at southern lowland Maya sites (NISP counts). ....................................................................................23 Table 3.1 Possible source location for local and exotic raw materials found at Pacbitun.47 Table 3.2 Vertebrate and invertebrate remains identified by Stanchly (1999) .................49 Table 4.1 Data and references for body mass of mammalian taxa at Pacbitun. ................63 Table 5.1 Taxonomic groups based on body size. ............................................................76 Table 6.1 Number of specimens by primary and secondary contexts for the Middle Preclassic assemblages. ......................................................................................................96 Table 6.2 Pre- and post-refit NISP counts by time period. ...............................................96 Table 6.3 Distribution of faunal remains by zoological class for the early and late Middle Preclassic samples at Pacbitun. ..........................................................................................97 Table 6.4 Identified taxa by NISP and MNI for the early and late Middle Preclassic samples at Pacbitun. ...........................................................................................................98 Table 6.5 Taxonomic representation in the Middle Preclassic samples by mesh size, in percentages. ......................................................................................................................104 Table 6.6 Bone density values of Rangifer tarandus compared to %NNISP and %MAU values for white-tailed deer long bone portions in the Middle Preclassic Pacbitun assemblages. .....................................................................................................................106 Table 6.7 Degree of post-depositional completeness by time period..............................110 Table 6.8 NISP counts for green- and dry-bone fractures by time period. .....................111 Table 6.9 Overall surface state for the Middle Preclassic Pacbitun assemblages. ..........112 Table 6.10 Percentage of observable surface in the Middle Preclassic samples. ............113 Table 6.11 Frequencies of cutmarks on identified specimens and indeterminate long bone shafts by overall surface state for the Middle Preclassic samples at Pacbitun. ...............114 Table 6.12 Frequencies of anthropogenic marks observed in the Middle Preclassic Pacbitun assemblages. ......................................................................................................115 x Table 6.13 Frequencies of carnivores marks observed in the Middle Preclassic Pacbitun assemblages. .....................................................................................................................117 Table 6.14 Extent of carnivore gnawing on bone surfaces for the Middle Preclassic samples at Pacbitun. .........................................................................................................118 Table 7.1 Skeletal part frequencies for white-tailed deer in the Middle Preclassic assemblages from Pacbitun ..............................................................................................127 Table 7.2 Skeletal part frequencies (NISP) of armadillo, peccary, and red brocket deer for the Middle Preclassic period at Pacbitun. ........................................................................128 Table 7.3 Number of specimens identified per category of epiphyseal fusion for whitetailed deer in the early and late Middle Preclassic samples at Pacbitun ..........................131 Table 7.4 Habitat fidelity values for the mammalian species identified in the Middle Preclassic assemblages at Pacbitun ..................................................................................140 Table 7.5 Analysis of habitat fidelity for the Pacbitun assemblages, by time period .....140 Table 7.6 Spearman’s rank order correlations between skeletal part representation and the MUI, grease index, and UMI. ..........................................................................................146 Table 7.7 Percentages of vertebrate taxa identified in Middle Preclassic assemblages at Pacbitun, Tolok group at Cahal Pech, Colha and Bayak .................................................154 Table 7.8 Results of the Kolmogorov-Smirnov tests for the Middle Preclassic assemblages from the southern lowlands. ........................................................................156 Table 7.9 Abundances of marine fish at southern lowlands Maya sites during the Middle Preclassic period, with average distances from the coast of the Caribbean Sea ..............158 xi 1 CHAPTER 1: INTRODUCTION For decades, archaeological research on the ancient Maya focused almost exclusively on documenting the ways of life of the Classic period (AD 300–900). Although these efforts contributed significantly to our understanding of the Maya, little was known about the early developments of this civilization during the Preclassic period (2000 BC–AD 250). This situation was also partly attributable to the Mesoamerican tradition of building new structures on top of older ones, which made it difficult for archaeologists to access Preclassic cultural remains, as they were often buried under meters of construction fill. However, in the past thirty years, more research projects have focused on documenting the social, political, and economic systems of the Preclassic Maya at sites such as Blackman Eddy (Garber et al. 2004a; Garber et al. 2004b), Cahal Pech (Healy and Awe 1995b, 1996; Powis et al. 1999; Healy et al. 2004), Cuello (Hammond 1991, 2005), Colha (Hester et al. 1982, 1994), and Cival (Estrada-Belli 2011). Unfortunately, growing interest in the excavations of Preclassic structures did not go in tandem with increased attention aimed at the recovery of faunal remains. As a result, the strategies of animal resource exploitation of the Preclassic Maya remain poorly documented. Several research projects have produced detailed analyses of animal procurement strategies for sites located in northern Belize (e.g., Shaw 1991; Masson 2004b; Carr and Fradkin 2008), but information for inland sites located in the Belize River Valley or the Peten region of Guatemala remains scarce. This problem is also exacerbated by the small sample size of many faunal assemblages, which often precludes detailed investigation of animal use during this early time period. 2 1.1 Research objectives The goal of this study is to contribute to filling this gap in research by investigating the strategies of animal resource exploitation adopted by the Preclassic Maya in the southern lowlands. This issue is examined using faunal remains recovered from Middle Preclassic (900–300 BC) deposits at Pacbitun, an ancient Maya site located at the southern rim of the Belize River Valley and occupied from the Middle Preclassic to Terminal Classic periods. Faunal remains recovered during the 1995 and 1996 field seasons have previously been presented in a preliminary report by Norbert Stanchly (1999). The present study includes the material from the 1997 and 2008–2011 excavations to provide a fuller archaeozoological analysis of the Middle Preclassic faunal remains from Pacbitun. The objectives of this analysis are as follows: 1) To complete a taphonomic analysis of the faunal remains and evaluate the impact of anthropogenic and natural agents on the assemblages; 2) To characterize the foraging strategies of the Maya of Pacbitun during the Middle Preclassic period through an investigation of diet breadth, habitat use, transport decisions, and skeletal part processing; 3) To consider how strategies of animal resource exploitation at Pacbitun contrast with that of other Middle Preclassic sites in the southern Maya lowlands. This study will examine the relationship that existed between the ancient Maya and the animal populations of the Belize River Valley during the Middle Preclassic. Additionally, this research will enhance our overall understanding of how the early Maya of the southern lowlands interacted with their environment. Although this research relies strictly on empirical faunal data to examine foraging strategies, the author would like to 3 remind that cultural beliefs about animals also play an important role in food choices and overall animal use. However, these considerations are outside the scope of this study. It should also be noted that the data presented in this study focus exclusively on the southern lowlands. Although more attention has recently been directed at documenting Middle Preclassic occupations in the northern lowlands (e.g., Rissolo et al. 2005; Stanton and Ardren 2005; Anderson 2011), information on the exploitation of animals resources in this region remains scanty. In fact, the only published faunal analysis of vertebrate remains known to the author from this region is that of Dzibilchaltun by Wing (1980). The sample for this site was considered too small (NISP = 53) to be included in this study. The next sections of this chapter provide general information on the Maya subarea and the cultural developments of the Middle Preclassic period. 1.2 The setting The ancient Maya inhabited the southeastern portion of Mesoamerica for over two millennia (2000 BC–AD 1500). During this period, the Maya subarea (Figure 1.1) encompassed southeastern Mexico, Guatemala, Belize, and the western regions of Honduras and El Salvador (Demarest 2004:11). The subarea is generally divided into three loosely defined environmental regions: the highlands, northern lowlands, and southern lowlands (Sharer 1994:20; Demarest 2004:121). The Maya highlands are formed by the mountainous region which stretches from the highlands of Chiapas, Mexico, to El Salvador. This region is characterized by valleys and basins of rich and fertile soils which lie above 800 m in elevation (Sharer 1994:26– 32; Demarest 2004:121). The northern lowlands are formed by the northern section of the Yucatan peninsula of Mexico and comprise the states of Campeche, Quintana Roo, and 4 Yucatan. The terrain is relatively flat, with the exception of the Puuc Hills. The region is characterized by a dry environment; there is little rainfall (500–2000 mm) and surface N Figure 1.1 Map of the Maya subarea including sites discussed in the present study. Map modified from Brown and Witschey (2008), retrieved from: http://mayagis.smv.org/maps_of_the_maya_area.htm. 5 water is generally scarce, with the exception of natural sinkholes. As a result, scrub vegetation prevails and soils are generally thin and show low fertility (Demarest 2004:120–127; McKillop 2004a:29–34). The southern lowlands—the focus of this study—separate the highlands from the northern lowlands and include the country of Belize, the Peten district of Guatemala, parts of Chiapas and lowland Honduras (McKillop 2004a:29). This region presents a more hilly terrain, with the Maya Mountains constituting the highest elevation on the landscape. The southern lowlands receive abundant rainfall (2000–3000 mm) and, as a result, are covered with lush rainforests. Large rivers and their tributaries also cover the landscape. These would have provided access to potable water and may have constituted important navigation routes in ancient times. Soils can be quite fertile in this region, especially in floodplains (Sharer 1994:34; Demarest 2004:120–127; McKillop 2004a:29– 34). 1.3 The Middle Preclassic period Despite its importance for understanding the origins of the Maya civilization, the Preclassic period (2000 BC–AD 250) is poorly documented in comparison to the Classic (AD 250–900) and Postclassic (AD 900–1525) periods (Powis 2005; Healy 2006). Archaeological evidence from the Early Preclassic (2000–1000 BC) indicates that a handful of farming villages were established in the southern lowlands at sites such as Cahal Pech, Nakbe, Seibal, Cival, Tikal, and Blackman Eddy (Figure 1.1). The architectural remains identified at these sites are modest (Estrada-Belli 2011). Domestic pole-and-thatch structures were generally erected directly on, or slightly above, the ground surface (Hansen 1998; Garber et al. 2004a; Healy et al. 2004). It is believed that 6 little social or economic differentiation existed within these communities, although larger villages might have been headed by a chief (Garber et al. 2004a; Healy et al. 2004). The farming village lifeway established during the Early Preclassic likely continued during the Middle Preclassic period (1000–300 BC). This latter period, however, was marked by the first indications of increased social and economic complexity, even though these signs are subtle at most sites (Healy 2006). In fact, the Middle Preclassic period may have coincided with a transition from a relatively egalitarian to a ranked society (Healy 2006). Most scholars divide the Middle Preclassic into two sub-periods: the early Middle Preclassic (1000–600 BC) and the late Middle Preclassic (600–300 BC). During the early Middle Preclassic, increasing complexity can be found in architecture, as wooden structures were being built on top of platforms made of modest stone walls and covered with plastered floors. These constructions were commonly organized around an open plastered-surface patio. It is believed that these clusters of structures functioned as residential groups, perhaps for an extended family (Hammond and Gerhardt 1990). Examples of these structures were found at Blackman Eddy (Garber et al. 2004a), Cahal Pech (Healy et al. 2004), Cuello (Hammond and Gerhardt 1990), and Nakbe (Hansen 1998), among others. The emergence of ritual ideology is possibly evidenced by the presence of dedication and termination caches in some of these structures (Garber et al. 2004a; Estrada-Belli 2011). Increasingly elaborate architecture also appears in the form of E-Groups at Seibal (Inomata et al. 2013), Tikal (LaPorte and Fialko 1995), and Cival (Estrada-Belli 2011). Considered as the first form of public architecture in the lowlands, the construction of these large structures demonstrates the ability of an emerging elite to marshal increasing amounts of labor (Estrada-Belli 2011). 7 It is hypothesized that E-Groups may have been constructed as a way to legitimize and express the political authority of new elite groups on the landscape (Doyle 2012). Signs of social and economic complexity became more apparent during the late Middle Preclassic, a period that witnessed the development of monumental public architecture at several sites, including Cahal Pech (Healy et al. 2004), Itzan (Johnston 2006), and Cuello (Hammond 1991, 2005). Large blocks of cut stones were used for the first time in the lowlands at Nakbe (Hansen 1998), whereas the first sculpted architectural decoration appeared in the form of stucco masks at Blackman Eddy (Garber et al. 2004a). These larger structures were some of the first occurrences of civic-ceremonial architecture and possibly served as places for public ritual and performance (Healy 2006). Trade networks within and outside the Maya subarea also intensified during the Middle Preclassic period. Exotic goods, such as greenstone, obsidian, and marine shells, were obtained from the Motagua Valley, Guatemalan highlands, and Caribbean coast (Garber et al. 2004a; Healy et al. 2004; Hammond 2005; Healy 2006). The early occurrence and diverse origins of these goods suggest the existence of extensive systems of long distance trade and exchange by the beginning of the first millennia BC. It should be noted that not all Middle Preclassic sites developed at the same rate. Indeed, many of the cultural developments mentioned above for the early Middle Preclassic only took place during the late Middle Preclassic or even the Late Preclassic periods at a majority of sites (e.g., Buenavista del Cayo, Ball and Taschek 2004). Overall, the religious, artistic, and architectural developments of the Middle Preclassic period appear to have provided a strong foundation for the political and cultural changes observed during the Late Preclassic (300 BC–AD 250). It is during this time period that we see throughout the Maya lowlands the first recognizable depictions of Maya kings and 8 the establishment of hereditary dynasties that would characterize the Maya civilization for centuries (Healy 2006; Estrada-Belli 2011). 1.4 Thesis overview This thesis is organized in eight chapters covering different aspects of my research. Chapter 2 offers a general overview of Maya subsistence strategies during the Middle Preclassic period. Chapter 3 introduces the site of Pacbitun and discusses the research conducted at the site. Chapter 4 reviews the foraging models used to interpret the faunal remains and provides a summary of the ecology and behavior of the prevalent animal species identified at the site. The methods used to quantify the faunal assemblages and assess the integrity of the samples are presented in Chapter 5, whereas Chapter 6 describes the samples analyzed in this study and considers the taphonomic history of the faunal remains. Chapter 7 presents the results of this study and discusses their implications for our understanding of animal resource exploitation at Pacbitun during the Middle Preclassic period. This chapter also considers how the faunal data align with research conducted at other Middle Preclassic sites in the southern lowlands. Lastly, Chapter 8 discusses the significance of the results and offers suggestions for future research. 9 CHAPTER 2: MIDDLE PRECLASSIC MAYA DIET This chapter provides a comprehensive account of previous research regarding Maya subsistence during the early developments of this civilization. It begins with a summary of Maya archaeozoology. The second half of this chapter presents the results of botanical, faunal, and isotopic studies relevant to the Maya diet during the Middle Preclassic period (1000–300 BC). 2.1 History of Maya archaeozoology The first archaeozoological studies in the Maya area were performed in the 1930s, when the Carnegie Institution of Washington and the Museum of Zoology of the University of Michigan jointly funded archaeological and biological research in British Honduras (modern-day Belize) and Guatemala (Chase et al. 2004; Emery 2004c, 2010). Alongside archaeological fieldwork, the emphasis was put on collecting biological specimens of vertebrate and invertebrate faunas of the Neotropics (Hubbs 1935; Murie 1935; Stuart 1935; van Tyne 1935; Goodrich and van der Schalie 1937) . The importance of animal resources for the ancient Maya was first discussed in excavation reports from the sites of Uaxactun (Ricketson 1937), Piedras Negras (Coe 1959), and Holmul (Merwin and Vaillant 1932). Early faunal studies were generally carried out by zoologists who limited their analysis to the taxonomic identification of specimens, producing species lists that were appended to site reports (Kidder et al. 1946:152–157; Moedano-Koer 1946; Woodbury and Trik 1954; Pina-Chan 1968). Typically, only specimens recovered from special deposits and artifacts made of bone and shell were analyzed. The results of the faunal studies were rarely integrated into interpretative frameworks (Emery 2004c, 2010). Although a considerable amount of 10 research was devoted to studying Maya subsistence strategies in the 1950s and 1960s, archaeozoological studies remained fairly limited in scope. Because it was largely assumed that animal proteins did not play an important role in the Maya diet, the study of animal resources was not considered an important avenue of research (Clutton-Brock and Hammond 1994; Emery 2004c, 2010). Under the influence of the “New Archaeology,” the analysis of faunal remains was progressively integrated into discussions regarding the paleoenvironment and subsistence of the ancient Maya (e.g., Savage 1971; Olsen 1972; Andrews et al. 1974; Luther 1974; Wing 1975; Pohl 1976; Olsen 1978; Hamblin 1984). Simultaneously, Maya archaeozoologists developed strategies to mitigate problems of sample recovery, preservation, and quantification (Clutton-Brock and Hammond 1994; Emery 2004c). As a result of these concerns, archaeologists began using finer mesh sieving (e.g., 1/8 and 1/16 inch mesh screen), which facilitated the recovery of fish and molluscs specimens from archaeological contexts. This, in turn, stimulated research on the importance of marine and riverine resources to the Maya diet (Moholy-Nagy 1963; Andrews 1969; Lange 1971; Moholy-Nagy 1978; McKillop 1984; Hamblin 1985; McKillop 1985; Moholy-Nagy 1985; Healy et al. 1990). Since the 1980s, archaeozoological studies form an integral component of most Maya archaeological projects. In addition to the study of subsistence and dietary adaptations to environmental changes (Carr 1985, 1986; Cliff and Crane 1989; Pohl 1990; Wing and Scudder 1991; Powis et al. 1999; Shaw 1999; Teeter 2001; Carr and Fradkin 2008; Götz 2008; Emery 2010), several new themes have emerged, such as the investigation of social structure and differential access to animal resources (Pohl 1994; Emery 1999; Shaw 1999; Teeter 2001; Collins 2002; Emery 2003; Götz 2009). The use 11 of animals in rituals and feasting has become a popular topic of study (Pohl 1981, 1983; Carr 1985; Pohl 1990; Masson 1999; Teeter 2001; Montero-Lopez 2009). Transport and exchange of animal resources are also investigated (Carr 1996; Emery 1999; Masson and Lope 2008; Thornton 2011), as well as the origins and process of animal domestication and husbandry (Hamblin 1984; Pohl 1990; Clutton-Brock and Hammond 1994; Carr 1996; Masson and Lope 2008). Isotopic analyses of animal remains have recently become an additional component of archaeozoological studies (Emery et al. 2000; White et al. 2001b; White 2004; Emery and Thornton 2008a; Repoussard 2009; Freiwald 2010; Thornton 2011). 2.2 Ancient Maya diet Information about the subsistence of the Maya during the Middle Preclassic period (1000–300 BC) is quite limited. This partly results from research biases, as archaeological projects in the study area have largely focused on the development of major centres during the Classic period (AD 300–900) (Healy and Awe 1995a; Healy 1999a; Powis 2005; Healy 2006). Additionally, organic remains are often scarce, perhaps due to unfavorable conditions of preservation. The following sections summarize our understanding of the Maya diet during the Middle Preclassic period by considering botanical, faunal, and isotopic data recovered from sites located in the southern lowlands. 2.2.1 Plant remains Ethnohistorical accounts (e.g., Tozzer 1941) indicate that the Maya diet was traditionally based on the exploitation of three cultigens: maize (Zea mays), beans (Phaseolus vulgaris), and squash (Cucurbita spp.). Together, they formed the Mesoamerican triumvirate (Turner and Miksicek 1984; Lentz 1999; Tykot 2002; Lentz et 12 al. 2005). Research conducted in the Maya subarea (Figure 1.1) suggests that maize and squash were domesticated around 3500 BC and 1500 BC, respectively (Pohl et al. 1996). The introduction of the common bean appears to date to the Middle Preclassic, although its utilization may be older (Lentz 1999; Lentz et al. 2005). The recovery of beans from the archaeological record is relatively sparse, possibly because they do not preserve well in the humid tropics (Lentz 1999). All three taxa have been recovered in Middle Preclassic deposits at southern lowland Maya sites (Table 2.1). Table 2.1 Plant remains recovered from Middle Preclassic deposits at southern lowland Maya sites. Taxon Triumvirate Maize Beans Squash Root crops Manioc Malanga Other plants Avocado Bottle gourd Cacao Cashew Chili peppers Coyol palm Fig Guava Hogplum Kinep Mamey Nance Ramón Cahal Pech x x x Pulltrouser Swamp Tikal x x x x x x x x x x x x x x x x x x x Colha Copan Cuello x x x x x x x x x x x x x x x x x x x x x x Source: Cahal Pech (Lawlor et al. 1995; Powis et al. 1999; Wiesen and Lentz 1999; Lentz et al. 2005), Colha (Turner and Miksicek 1984; Jones 1994), Copan (Turner and Miksicek 1984; Lentz 1991), Cuello (Miksicek et al. 1981a; Miksicek 1991), Pulltrouser Swamp (Turner and Miksicek 1984; Pohl et al. 1996), Tikal (Turner and Miksicek 1984). 13 In addition to the triumvirate, the Maya relied on tree cropping (Puleston 1982; Turner and Miksicek 1984; Lentz 1991), as is attested by the recovery of archaeobotanical remains of domesticated fruit trees, such as the avocado (Persea americana), cashew (Anacardium occidentale), and cacao (Theobroma cacao) (Lentz 1999) (Table 2.1). A variety of fruits, including the fig (Ficus spp.), guava (Psidium guajava), hogplum (Spondias mombin), kinep (Talisa oliviformis), mamey (Calocarpum mammosum), and nance (Byrsonima crassifolia), as well as chili peppers (Capsicum annuum), were likely exploited for food (Roys 1931:346–348; Turner and Miksicek 1984; Miksicek 1991; Lentz 1999; Powis et al. 1999; Wiesen and Lentz 1999; Colunga-García Marín and Zizumbo-Villarreal 2004; Lentz et al. 2005). These were likely cultivated in orchards and gardens (Turner and Miksicek 1984; Lentz 1991, 1999) or gathered in the forest (Lentz 1999). Although Bronson (1966) has argued that root crops might have been important staples in Maya agriculture, the degree to which they contributed to the Maya diet is still debated (Lentz 1999). Sweet potato (Ipomoea batatas), yam bean (Pachyrhizus erosus), malanga (Xanthosoma sp.), and manioc (Manihot esculenta) are frequently mentioned in ethnohistoric records (e.g., Roys 1931:346; Tozzer 1941:196). However, they are rarely recovered from archaeological sites, again likely due to poor preservation (Turner and Miksicek 1984; Hather and Hammond 1994; Lentz 1999). Certain plants, such as the coyol (Acrocomia aculeata), cohune (Attalea cohune), and ramón (Brosimum alicastrum), were possibly consumed during times of famine (Tozzer 1941:200; Miksicek et al. 1981b; Marcus 1982; Turner and Miksicek 1984; Lentz 1991; McKillop 1996; Lentz 1999; Wiesen and Lentz 1999). In addition to being exploited for food, many of these plants 14 may have been used as medicine, animal fodder, and construction material (Roys 1931; Tozzer 1941). 2.2.2 Animal resources Animal species diversity in the Maya subarea is one of the richest in the world (Emmons 1997; Emery 2010:45). Archaeological, ethnohistoric, and iconographic evidence indicates that animals had both socioeconomic and symbolic importance for the residents of this region from the Late Preclassic to Colonial periods (Tozzer 1941; Pohl 1983; Hamblin 1984; Emery 2010). However, during the Middle Preclassic, animals seem to have been used primarily for food and utilitarian purposes (Willey 1978; Pohl 1990; Shaw 1991; Wing and Scudder 1991; Stanchly 1995; Moholy-Nagy 1998; Powis et al. 1999; Harrigan 2004; Masson 2004a, 2004b; Carr and Fradkin 2008; Emery 2010). It is probable that the Middle Preclassic Maya made use of animals for religious purposes, but little archaeological data is currently available to support this idea. One of the only examples come from Cahal Pech, where several hundred complete specimens of apple snails were discovered in a cache (Stanchly 1995). At Blackman Eddy, a concentration of faunal remains associated with multiple serving vessels was interpreted as the remnants of a feasting event (Brown 2007). Therefore, in order to present a complete range of the possible roles animals may have played in the Middle Preclassic society, this section presents the main taxa exploited by the ancient Maya, including information on the use of animals in rituals from later time periods. 15 Artiodactyls were among the most valuable animal resources used by the ancient Maya. The white-tailed deer (Odocoileus virginianus)1, red brocket deer (Mazama americana), collared peccary (Pecari tajacu), and white-lipped peccary (Tayassu pecari) are the most common taxa recovered in Middle Preclassic deposits (Pohl 1990; Shaw 1991; Wing and Scudder 1991; Stanchly and Dale 1992; Stanchly 1995; Powis et al. 1999; Carr and Fradkin 2008; Emery 2010). They seem to have been a favoured source of food and raw material (Tozzer 1941:204; Pohl 1990; Hopkins 1992; Carr 1996; Teeter 2001:215–217; Emery 2010). Specifically, the white-tailed deer is regarded as the main animal staple in the Maya diet (Pohl 1990; Emery 2010). Commonly used in sacrifices during the Classic and Postclassic periods, deer legs and heads, as well as peccary heads, are depicted as offerings in the Maya codices2 (Tozzer and Allen 1910; Tozzer 1941:115, 163–165; Pohl 1983). Deer skulls were also recovered in ritual caches dating to the Late Preclassic at Cuello (Wing and Scudder 1991). Ethnohistoric accounts suggest that the Postclassic Maya managed deer and peccary herds (Tozzer 1941:127; Hamblin 1984:132–133; Donkin 1985; Carr 1996). It is believed that this activity involved feeding the animals with significant quantities of maize (Emery et al. 2000; van der Merwe et al. 2000). However, stable isotope analyses of carbon and nitrogen on deer and peccary bones do not support this hypothesis for the Middle Preclassic period, as both species exhibit a diet composed predominantly of wild plants (Tykot et al. 1996; Emery et al. 2000; van der Merwe et al. 2000; White et al. 2001b). 1 Latest taxonomic nomenclature retrieved from the Integrated Taxonomic Information System (www.itis.gov, accessed March 28, 2013). 2 The Maya codices are screen-fold books written by the ancient Maya during the Late Postclassic period (AD 1250–1520). The books are made of bark paper on which glyphs and pictures were painted. They record ritual and astronomical information (Vail and Aveni 2004). 16 Dogs (Canis lupus familiaris) seem to have been the only domesticated animal sued by the Maya during the Middle Preclassic, likely serving both as pets and hunting companions (Tozzer 1941:203; Hamblin 1984; Pohl 1990; White et al. 2001b). Associated with death and the journey to the underworld, dogs played a large role in Maya religion during the Classic and Postclassic periods. For instance, they were frequently offered as sacrificial victims in rites associated with annual renewal ceremonies (Tozzer and Allen 1910; Tozzer 1941:143; Pohl and Feldman 1982; Pohl 1983; Hamblin 1984:117–120; White et al. 2001b). Dog skulls and teeth were also recovered as offerings in burial contexts dating to the Late Preclassic (Carr 1986:254; Valdez 1995). In a society where hunting was the primary means of acquiring proteins and fats, domesticated dogs possibly constituted a reliable source of food when other resources were scarce (Tozzer 1941:203; Pohl 1990; Clutton-Brock and Hammond 1994; White et al. 2001b). Stable isotope analyses conducted on dog remains recovered from middens dating to the Middle Preclassic period showed large variations in results, suggesting that dogs were not fed a stable household diet, but more likely scavenged, hunted, and foraged on their own (Tykot et al. 1996; van der Merwe et al. 2000; White et al. 2001b). Dogs recovered from special deposits, however, contrast with other dogs as their diet was rich in maize. It was suggested that these animals may have been purposefully fattened for sacrificial purposes (Tykot et al. 1996; White et al. 2001b). Another canid, the gray fox (Urocyon cinereoargenteus), is also present in the Maya subarea and might have been hunted for its pelt (Teeter 2001) and for food (Hamblin 1984:151–152). Some small game species also seem to have been economically important for the Maya during the Middle Preclassic (Pohl 1990; Shaw 1991; Wing and Scudder 1991; Stanchly and Dale 1992; Stanchly 1995; Powis et al. 1999; Masson 2004a; Carr and 17 Fradkin 2008; Emery 2010). The armadillo (Dasypus novemcinctus) was probably hunted for its meat as well as for its carapace, which might have been used as a container or instrument (Tozzer 1941:204; Hopkins 1992; Emery 2010). Rabbits, including the cottontail (Sylvilagus floridanus) and forest rabbit (S. brasiliensis), may have been exploited for their meat and pelt (Tozzer 1941:204; Hopkins 1992; Emery 2010). Two large rodents, the agouti (Dasyprocta punctata) and paca (Cuniculus paca), were also probably hunted for their fatty meat (Stuart 1964; Hopkins 1992; Emery 2010). The use of other mammals as a source of food is speculative. Only identified at a handful of Middle Preclassic sites (see Wing and Scudder 1991; Shaw 1999; Carr and Fradkin 2008), it is uncertain if the pocket gopher (Orthogeomys hispidus) was considered as a food source or if it is intrusive to the archaeological record (Hopkins 1992; Emery 2010). Other rodents, such as rats and mice, are more likely to have entered archaeological deposits on their own, given that they often live in burrows (Pohl 1983; Emery 2010). Pohl (1983), however, suggests that they might have held some symbolic importance for the Maya because of their occasional occurrence in ceremonial deposits. Ethnohistoric accounts indicate that the common opossum (Didelphis marsupialis) and Virginia opossum (D. virginiana) were used as food sources (Hamblin 1984:154; Teeter 2001; Emery 2010). Similarly, Bishop de Landa reports that the Maya occasionally hunted tapirs (Tozzer 1941:203). Procyonids, including raccoons (Procyon lotor), kinkajous (Potos flavus) and coatis (Nasua narica), are frequent agricultural pests today and, perhaps for this reason, were often used to depict human thieves and gluttons in the Maya codices (Tozzer 1941:205; Emery 2010). Landa reports that coatis were raised by Maya women as pets and were sometimes eaten (Tozzer 1941:204–205; Hamblin 18 1984:147–149). Although all these animals seem to have been exploited during the Postclassic and Colonial periods, their use during the Middle Preclassic is unclear. Felines, including the puma (Puma concolor), jaguarundi (Puma yagouaroundi), margay (Leopardus wiedii), and ocelot (Leopardus pardalis), played an essential role in Maya religion and were often sacrificed in ceremonies during the Classic and Postclassic periods (Tozzer 1941:163; Hopkins 1992). The jaguar (Panthera onca), in particular, has long been associated with sorcery and the supernatural underworld (Tozzer and Allen 1910:355–358; Pohl 1983; Hamblin 1984:164; Emery 2010). Jaguar skins and teeth were important status markers during the Classic period. Priests and rulers appear to have worn them as a sign of their divine power (Pohl 1983; Hopkins 1992; Emery 2010), whereas lesser elites may have used ocelot and margay skins as a display of their status (Emery 2010). It is not known if felines were used in a similar fashion during the Middle Preclassic period. Galliforms, including the curassow (Crax rubra), crested guan (Penelope purpurascens), and ocellated turkey (Meleagris ocellata), were probably the most important birds used as food sources (Hamblin 1984; Emery 2010:91). Also possibly hunted for meat were the ground-dwelling tinamous (Tinamidae), ducks and their relatives (Anatidae), herons (Ardeidae), cranes (Gruidae), rails (Rallidae), pigeons and doves (Columbidae) (Tozzer 1941; Shaw 1991:201–203). Although none of these birds, with the exception of the wild turkey (Meleagris gallopavo), were domesticated at the time of conquest, ethnohistoric sources suggest that birds were occasionally captured and penned. The Maya may also have stolen eggs from nests in order to raise the chicks (Tozzer 1941:202; Hamblin 1984:93–94). Many birds, the turkey above all, held special symbolic importance for the Classic and Postclassic Maya. Parts from these birds were 19 repeatedly used as offerings or deposited in caches and burials (Tozzer and Allen 1910:325–327; Tozzer 1941; Pohl 1983; Hamblin 1984:95; Emery 2010), while colorful feathers were used to decorate clothing, headdresses, and banners (Tozzer 1941:89; Hamblin 1984:95; Emery 2010). Although they possibly represented a valuable source of food, bird remains are usually rare at Maya sites, perhaps because their fragile bones do not preserve well in tropical environments. Disagreement generally surrounds the interpretation of amphibians recovered from Maya sites. Although some pre-Hispanic groups, such as the Campa and Wayapi, seem to have eaten frogs and toads, there is no solid archaeological or ethnohistoric evidence that the Maya consumed amphibians (Hamblin 1984; Teeter 2001). Several authors have suggested that these animals might have been associated with shamanistic rituals and that a poison secreted by the marine toad (Rhinella marina) may have been used as a hallucinogenic drug (Hamblin 1984:53–57; Emery 2010). Because of their rarity at archaeological sites and their tendency to dig burrows, many of the amphibians recovered from Maya sites are believed to be intrusive (Wing and Scudder 1991; Carr and Fradkin 2008; Emery 2010). Many reptile taxa had both an economic and ceremonial role for the Classic and Postclassic Maya. Crocodiles (Crocodylus sp.) were seen as lords of the underworld (Tozzer and Allen 1910; Emery 2010). They were offered in sacrifices and are frequently depicted in the Maya codices (Tozzer 1941; Pohl 1983:163; Thurston 2011). Snakes, associated with water and fertility, held important ceremonial role and were often depicted in scenes of blood sacrifice in Classic Maya art (Pohl 1983; Emery 2010). Iguanas, either of the green (Iguana iguana) or black (Ctenosaura similis) variety, were prized for food in Postclassic and historic times (Tozzer 1941:191; Stuart 1964; Hamblin 20 1984:68–69; Emery 2010). They are often represented in the codices as sacrificial offerings (Tozzer and Allen 1910; Emery 2010:318). It is difficult to form conclusions about the use of these reptiles during the Middle Preclassic because their remains are seldom recovered in archaeological deposits from this time period. Ethnohistoric accounts indicate that both freshwater and marine turtles were valued for their meat and eggs, as well as their carapaces, which could be used as rattles, drums, shields, and containers (Tozzer and Allen 1910; Tozzer 1941:114, 192; Stuart 1964; Emery 2010). Turtles represent one of the most abundant taxa in Middle Preclassic assemblages and, therefore, it has been suggested that the Preclassic Maya subsisted heavily on turtles (Shaw 1991; Stanchly 1995; Powis et al. 2002; Fradkin and Carr 2003). Common species include the mud turtles (Kinosternon spp.), giant musk turtle (Staurotypus triporcatus), common slider turtle (Trachemys scripta) and Central American river turtle (Dermatemys mawii). Fish probably constituted another source of proteins and fats for the Preclassic Maya (Tozzer 1941:190–191; Hamblin 1984). Freshwater fish, such as the catfish (Ictaluridae), mojarra (Cichlasoma spp.) and swamp-eel (Synbranchus marmoratus), were possibly locally available at most Maya sites (Powis et al. 1999; Powis et al. 2002; Fradkin and Carr 2003; Carr and Fradkin 2008; Emery 2010). During the Middle Preclassic, marine fish, including the bonefish (Albula vulpes), parrotfish (Scaridae), snapper (Lutjanidae) and jack (Carangidae), were sometimes imported to inland sites over considerable distances (>100 km) (Powis et al. 1999; Powis et al. 2002). During the Classic period, marine fish bones and stingray spines were used in ceremonies performed by the elite, particularly for bloodletting rituals (Pohl 1983; Emery 2010). 21 Freshwater molluscs commonly found at archaeological sites included the gastropods apple snail (Pomacea flagellata) and jute (Pachychilus spp.), as well as the pearly mussel (Nephronaias spp.). Although they are occasionally eaten by the modern Maya (Moholy-Nagy 1963, 1978; Healy et al. 1990), the frequency with which freshwater molluscs were consumed by the ancient Maya is debated (Covich 1983; Stanchly 1995; Solis 2011). Their low nutritional returns suggest that they served at best as a supplementary source of food (Moholy-Nagy 1978; Powis 2004; Solis 2011). In archaeological settings, freshwater shells are often fashioned into utilitarian and ornamental artifacts (Moholy-Nagy 1963, 1978; Healy et al. 1990; Stanchly and Dale 1992; Harrigan 2004; Emery 2010). Frequently recovered in caches and burials from the Late Preclassic onwards, they might have played an important role in ceremonies and mythology (Moholy-Nagy 1963, 1978; Harrigan 2004). Marine molluscs were considered symbols of death and rebirth and often used for ceremonial and ornamental purposes from the Late Preclassic to Postclassic periods (Moholy-Nagy 1963; Pohl 1983; Moholy-Nagy 1985; Hohmann 2002). During the Classic period, the most highly valued ceremonial molluscs were the colorful spiny oyster (Spondylus spp.), olive (Oliva spp.), conch shell (Strombus spp.) and marginella (Prunum apicinum) which were often worked into jewelry and decorative objects (Tozzer 1941; Moholy-Nagy 1985; Harrigan 2004; Emery 2010). During the Middle Preclassic, marine shells were imported from the coast to inland sites for the manufacture of ornaments (Lee and Awe 1995; Hohmann 2002). It is not clear if the animal was consumed in the process (Powis et al. 1999). 22 2.2.3 Middle Preclassic use of animals The dominant foraging strategy during the Middle Preclassic involved hunting, fishing, and collecting animals procured in the immediate vicinity of the sites. Animal use included the exploitation of terrestrial animals, particularly white-tailed deer, brocket deer, armadillo, peccary, agouti, rabbit, and opossum (Pohl 1990; Shaw 1991; Wing and Scudder 1991; Stanchly 1995; Moholy-Nagy 1998; Powis et al. 1999; Masson 2004a, 2004b; Carr and Fradkin 2008; Emery 2010) (Table 2.2). In northern Belize, the Middle Preclassic Maya also seem to have relied on the exploitation of mud and musk turtles, which they likely acquired in the wetland areas surrounding the sites (Wing and Scudder 1991; Fradkin and Carr 2003; Masson 2004a, 2004b; Carr and Fradkin 2008). Archaeological evidence suggests that dogs were likely consumed as food (Pohl 1990; Shaw 1991; Wing and Scudder 1991; Clutton-Brock and Hammond 1994; Masson 2004a). At Cuello, the average mortality age of dogs (around one year old) coupled with a high frequency of spiral fractures on green bone and cutmarks support the theory of regular consumption of dogs by the Preclassic Maya (Clutton-Brock and Hammond 1994). The Preclassic Maya likely practiced a modified form of “garden hunting” (Linares 1976), which involved the procurement of animals near milpas. Most of the animals frequently identified in faunal assemblages are known to visit open clearings and cultivated fields (Pohl 1990; Masson 2004a, 2004b; Carr and Fradkin 2008; Emery 2010). The presence of the brocket deer, tapir, and paca—animals that thrive in undisturbed dense forests—also indicates that hunting trips were occasionally taken to forested areas (Pohl 1990; Shaw 1999; Masson 2004a; Carr and Fradkin 2008). Table 2.2 List of identified taxa recovered from Middle Preclassic deposits at southern lowland Maya sites (NISP counts). Scientific Name MAMMALS Didelphis spp. Dasypus novemcinctus Canidae Canis lupus familiaris Urocyon cinereoargenteus Procyon lotor Mustela frenata Galictis sp. Felidae Tapirus bairdii Artiodactyla Cervidae Odocoileus virginianus Mazama americana Tayassuidae Pecari tajacu Tayassu pecari Rodentia Dasyproctidae/Cuniculidae Cuniculus paca Dasyprocta punctata Geomyidae Orthogeomys hispidus Sylvilagus spp. BIRDS Galliformes Meleagris ocellata Common Name Opossum Armadillo Dog, fox, coyote Domestic dog Gray fox Raccoon Long-tailed weasel Grison Felines Tapir Cervids White-tailed deer Red brocket deer Peccaries Collared peccary White-lipped peccary Agouti and paca Paca Agouti Pocket gophers Hispid pocket gopher Rabbits Ocellated turkey Northern Belize Central Belize Cuello Colha K’axob Cahal Pech 69 1007 10 381 15 16 4 2 4 6 261 698 78 42 5 1 44 1 23 32 19 2 152 6 7 11 12 34 298 11 Petén Altar de Bayak Seibal Sacrificios 26 4 17 2 4 9 2 1 1 1 27 68 2 1 4 17 1 1 5 31 2 5 10 1 1 13 28 3 6 3 1 1 59 2 3 2 5 2 15 2 7 2 1 1 13 1 2 23 Scientific Name Other birds Unidentified birds AMPHIBIAN Ranidae Rhinophrynus dorsalis Rhinella marina REPTILES Testudines Dermatemys mawii Emydidae Trachemys scripta Rhinoclemmys areolata Kinosternidae Claudius angustatus Kinosternon spp. Staurotypus triporcatus Chelydra serpentina Serpentes Colubridae Viperidae Crotalinae Iguanidae Crocodylidae FISH Marine fish Ariidae Albula vulpes Carangidae Gerreidae Gobiomorus dormitor Lutjanidae Common Name Northern Belize Central Belize Cuello Colha K’axob Cahal Pech 10 17 Frogs Mexican burrowing toad Marine toad Turtles Central American river turtle Pond turtles Terrapin/bokatora Furrowed wood turtle Mud and musk turtles Narrow-bridged musk turtle Mud turtles Mexican giant musk turtle Common snapping turtle Snakes Colubrids Vipers Rattle snakes Iguanas Crocodiles Sea catfish Bonefish Jack Marine mojarra Bigmouth sleeper Snappers 6 4 29 32 3 88 70 103 31 15 46 68 708 8 6 6 3 2 4 5 4 3 3 54 Petén Altar de Bayak Seibal Sacrificios 39 2 1 12 160 63 5 1 13 10 1 2 16 4 1 8 16 2 3 2 1 1 2 182 4 6 2 3 4 1 2 41 1 24 Scientific Name Common Name Scaridae Scarus spp. Sparisoma spp. Serranidae Freshwater fish Ictaluridae Cichlidae Cichlasoma spp. Synbranchus marmoratus Unidentified fish MOLLUSCA Freshwater shellfish Pachychilus spp. Pomacea flagellata Psoronaias spp. Nephronaias ortmanni Marine shellfish Strombidae Strombus spp. Prunum spp. Oliva spp. Dentalium spp. Parrotfish Parrotfish Parrotfish Grouper Catfish Cichlids Cichlid (mojarras) Swamp eel Jute Apple snail River clam Pearly mussel Strombus Queen conch Marginella Olive Tusk shell Northern Belize Central Belize Cuello Colha K’axob Cahal Pech 6 1 18 1 1 13 37 19 30 532 3 9 4 1 Petén Altar de Bayak Seibal Sacrificios 8 3 6 2 633 643 2076 80 – – – – 418 3327 813 315 4085 – – – – 1054 68 4 2 22 – – – – – – – – – – 8 399 3 3 58 14 Source: Cuello (Miksicek 1991; Wing and Scudder 1991; Clutton-Brock and Hammond 1994; Carr and Fradkin 2008), Colha (Shaw 1999), K’axob (Harrigan 2004; Masson 2004a), Cahal Pech (Stanchly and Dale 1992; Stanchly 1995; Powis et al. 1999), Altar de Sacrificios (Pohl 1990), Bayak (Emery 2010), Seibal (Feldman 1978; Pohl 1990). – No data available. 25 26 Freshwater molluscs are not particularly abundant at Middle Preclassic sites, with the exception of Cahal Pech. These molluscs might have served as a supplementary source of food (Miksicek 1991; Stanchly 1995; Powis et al. 1999; Harrigan 2004), although their importance to the Maya diet is difficult to assess because they were not considered in the faunal analyses of Colha, Altar de Sacrificios, and Seibal. These animals could also have been used in the production of shell ornaments (Wing and Scudder 1991). Similarly, the interpretation of fish remains is limited by the difficulty of identifying tropical fish taxa (Stanchly 1995; Powis et al. 1999). Among these, it should be noted that freshwater fish (e.g., cichlids, catfish) could have been exploited within a radius of 10 km at all sites (Shaw 1991; Wing and Scudder 1991; Masson 2004a; Emery 2010). The near absence of fish bones at Seibal and Altar is unexpected, because both sites sit on the banks of the Pasión River. This pattern may result from the recovery strategy adopted during the excavations, as sediments were not sieved at the site (Pohl 1990). The minor representation of marine fish (e.g., bonefish, parrotfish, jack, and snapper) suggests that animal products were sometimes procured from considerable distance, but they do not seem to have been dietary staples at the sites (Shaw 1991; Wing and Scudder 1991; Stanchly 1995; Fradkin and Carr 2003; Masson 2004a; Carr and Fradkin 2008). The inhabitants of Cuello, Colha, and K’axob may have acquired fish from Chetumal Bay (35 km to the north) or the Caribbean Sea (50 km to the east) (Wing and Scudder 1991; Fradkin and Carr 2003; Masson 2004a; Carr and Fradkin 2008). The presence of fish at the inland site of Cahal Pech indicates transport over a distance of at least 100 km (Stanchly 1995; Powis et al. 1999; Powis et al. 2002). Fish may have been 27 smoked or salted for inland transport, or kept alive in containers filled with water (Stanchly 1995; Powis et al. 1999; Powis et al. 2002). Likewise, marine molluscs (e.g., olive, marginella, thorny oyster, and conch shells) represent a very small component of the assemblages, with the exception of Cahal Pech. It has been suggested that marine shells were acquired for the manufacture of artifacts (Wing and Scudder 1991; Lee and Awe 1995; Stanchly 1995; Powis et al. 1999), which might have involved consumption of the associated meat (van der Merwe et al. 2000). The presence of marine species at Middle Preclassic sites is frequently attributed to the direct exploitation of the coastal environment or the existence of exchange networks (Shaw 1991; Stanchly 1995; Powis et al. 1999; Powis et al. 2002). Animals from remote habitats are nearly absent from the sites in the Petén region (Altar de Sacrificios, Bayal, Seibal, and Tikal), with the exception of a stingray spine recovered from a burial at Tikal (Moholy-Nagy 1998). 2.2.4 Stable isotope analysis Animal and plant remains recovered from archaeological sites are useful for determining the types of resources available to the ancient Maya. Stable isotope analysis can add to these results by determining which foods were consumed and in what proportions. More precisely, stable isotope analysis of human bones can help detecting the consumption of maize (a C4 plant) in comparison to C3 plants (e.g., root crops, fruits, nuts, legumes, and vegetables), as well as determining the main sources of proteins (terrestrial versus aquatic resources) in the diet. Stable isotope studies from Middle Preclassic sites suggest considerable dietary heterogeneity between sites located in Belize versus the Petén region (White and 28 Schwarcz 1989; Tykot et al. 1996; White 1997; Wright 1997, 2006). Such variation has been attributed to differences in local ecology and population density (van der Merwe et al. 2000; Wright 2006:196). People at sites located in the Petén (i.e., Seibal and Altar de Sacrificios) are believed to have relied heavily on maize and animals characterized by a diet rich in C4 plants. These include domestic dogs and animals that may browse in agricultural fields, such as deer and peccaries (Wright 1997, 2006). The high nitrogen values observed in the analyses may be indicative of the consumption of large quantities of terrestrial herbivores as well as freshwater fish (Wright 2006:192–196). In comparison, the Preclassic Maya living in northern Belize apparently subsisted on a broader diet, consuming a wider range of plant foods and animal resources (van der Merwe et al. 2000; Wright 2006). Consistently more negative collagen values at Belizean sites suggest a greater access to plants other than maize relative to the Petén region (White and Schwarcz 1989; Henderson 1998; Coyston et al. 1999; Henderson 2003). The range of carbon and nitrogen values may indicate that a variety of terrestrial animals, such as deer, dog, and peccary, constituted the main protein sources, with the possible addition of turtles (White and Schwarcz 1989; Tykot et al. 1996; Henderson 1998). The stable isotope analyses reveal that marine and reef resources do not seem to have contributed substantially to the diet in northern Belize. This result is not unexpected considering that all three sites are located approximately 50 km inland (White and Schwarcz 1989; Henderson 1998; van der Merwe et al. 2000; Young 2002; Hammond and Young 2003; Henderson 2003). Small amounts of freshwater fish, however, were presumably consumed at Cuello (Young 2002:117–118; Hammond and Young 2003) and Lamanai (White and Schwarcz 1989). 29 Located only seven km from the Caribbean Sea, the residents of Altun Ha seem to have relied heavily on the exploitation of the coastal environment. Stable isotope analyses suggest that marine and reef resources likely constituted the main protein sources at the site (White et al. 2001a). This interpretation is supported by the recovery of many vertebrate and molluscan marine remains (Pendergast 1979:7–12). Maize is argued to have formed the main dietary staple, with the addition of other wild and cultivated plants (White et al. 2001a). At Cahal Pech, in central Belize, the carbon and nitrogen isotopic values are similar to those observed at inland sites in northern Belize. This further supports the argument that maize represented a significant, but not dominant, component of the diet during the Middle Preclassic (Powis et al. 1999). Combined carbon and nitrogen values suggest that terrestrial herbivores were consumed as well as reef fish. This last result is surprising because the frequent consumption of marine fish seems incompatible with the location of the site (Powis et al. 1999). 2.3 Summary Faunal, paleobotanical, and isotopic data recovered from sites in the southern Maya lowlands points to a broad-based subsistence pattern during the Middle Preclassic period. The ancient Maya were relying heavily on cultivated plants, such as maize, squash, and beans, which they supplemented with an assortment of fruits, root crops, and vegetables. They consumed wild game and domesticated animals, as well as invertebrates and wild plants. The next chapter turns to a description of the research undertaken at Pacbitun. 30 CHAPTER 3: SITE DESCRIPTION AND PREVIOUS RESEARCH This chapter provides contextual information about the ancient Maya site of Pacbitun. It begins with a description of the environmental setting and geographic location of Pacbitun. Then, the various archaeological excavations carried out at the site are described, followed by a presentation of the history of occupation of Pacbitun. The chapter concludes with a description of the architectural remains and artifactual assemblages dating from the Middle Preclassic period, and a discussion of local subsistence practices. 3.1 Geographical context Pacbitun is a medium-sized center located within the southern Maya lowlands, in west-central Belize. It lies on the southern edge of the upper Belize River Valley, three kilometers east of the modern village of San Antonio (Figure 3.1). The site was occupied between 900 BC and AD 900 and is one of many centers that flourished during the Classic period (AD 300–900) in the Belize River Valley (Healy et al. 2004b; Healy et al. 2007). Pacbitun’s location on the southern rim of the Belize River Valley, at the junction of two ecozones, namely the lowland tropical rainforest and the upland pine ridge, made it unique from other sites in the area. It has been suggested that this location was chosen by the early Maya to take advantage of the locally contrasted microenvironments and their diverse resources (Graham 1987; Campbell-Trithart 1990; Healy 1990a). The lowland tropical rainforest borders Pacbitun to the west, north, and east. This ecozone is 31 Figure 3.1 Map of the Belize Valley (modified from Chase and Garber 2004:2). characterized by a dense tropical broadleaf forest which provides a habitat for numerous animals (e.g., agouti, coati, white-lipped peccary, curassow, and red brocket deer) (Schlesinger 2001). Around Pacbitun, fertile soils are found in natural catchment basins and depressions created by the hilly terrain (Wright et al. 1959:190–191; Healy 1990a; Sunahara 1995; Healy et al. 2007). Further south, the tropical rainforest gives way to the Mountain Pine Ridge (Figure 3.2), an ecozone that is sparsely covered with highland oak and pine. The lack of cultivable lands in this region has limited permanent habitation by the ancient Maya, although they likely exploited other resources, such as granite, slate, and pinewood (Wright et al. 1959:171–175; Graham 1987; Healy 1990a). 32 Figure 3.2 Location of Pacbitun in the Upper Belize Valley (Hohmann and Powis 1999:2). The Pacbitun Maya also had access to the Belize River and its two principal tributaries, the Mopan (Western Branch) and Macal (Eastern Branch) Rivers. In addition, multiple secondary and tertiary streams are found within kilometers of the site, such as Barton Creek, Slate Creek, Tutu Creek, and Privassion Creek (Figure 3.2) (CampbellTrithart 1990; Hohmann and Powis 1999). This river system provided the ancient Maya with continuous access to aquatic resources, such as fish, molluscs, waterfowl, iguanas, and turtles (Hohmann 2002:61), and facilitated the transportation of goods from the Caribbean Sea to the interior of the Maya subarea (Willey et al. 1965; Chase and Garber 2004). Settlement surveys at Pacbitun also revealed the existence of permanent water springs and a major reservoir near the site (Healy et al. 2007). 33 Pacbitun is located within the tierra caliente (“hot land”) zone of the tropics (West and Augelli:46). In this tropical to sub-tropical climate, temperatures are nearly constant throughout the year, ranging between 25–30°C (Wright et al. 1959; West and Augelli 1966). The climate is also characterized by distinct dry and wet seasons. In the San Antonio sub-region where the site of Pacbitun is located, the dry season lasts from January to April, whereas the wet season occurs between May and December. This subregion receives about 125–175 cm of rainfall per year (Wright et al. 1959). Palaeoclimate records from the lakes of Punta Laguna (Curtis et al. 1996) and Chichancanab (Hoddell et al. 1995), in northern Yucatan Peninsula, suggest that the climate during the Middle Preclassic was slightly wetter than today. The central precinct of Pacbitun lies 240 meters above sea level and sits atop a limestone plateau that is oriented east-west. This elevated position in the landscape provided a peripheral view of the hilly terrain surrounding the site, which can be divided into three zones: the epicenter, the core zone, and the periphery (Figure 3.3). Research suggests that the epicenter (0.5 km2) formed the religious and political heart of Pacbitun during the 2000 years of occupation of the site (Healy et al. 2007:17–18). The current configuration of this zone consists of 40 masonry structures, including temple-pyramids, palace-like range structures, one ball court, two causeways, and 20 whole and partial stelae and altars (Figure 3.4). It also contains three major (A, B, and C) and two secondary (D and E) plazas, the latter located to the north of the main site axis, and a number of smaller courtyard groups. During the Classic period, the use of the epicenter was likely restricted to the elite class, with few exceptions (Bill 1987; Healy 1990a; Healy et al. 2007). 34 Epicenter Core Zone Periphery Zone Figure 3.3 Map of the Pacbitun settlement survey. The concentration of monumental architecture in the center of the map forms the epicenter. The dashed square around the epicenter coincides with the 1 km2 core zone. The four dashed rectangles delineate the periphery zone. All architectural remains are drawn in black. Shaded circular areas are possible reservoirs (modified from Healy et al. 2007:20). The core zone includes the epicenter as well as small, medium, and large mounds constructed within an area of 1 km2 from Plaza A (Figure 3.5). The earthen mounds are the remains of domestic structures that are generally considered residences for lesser-elite or non-elite individuals living outside the epicenter (Campbell-Trithart 1990:319–322; Healy et al. 2007). The periphery zone surrounds the core zone and covers an additional 8 km2 (Figure 3.3). This zone was probably the sustaining agricultural area of Pacbitun. It is 35 Figure 3.4 Plan of the epicenter of Pacbitun. Structures are shown as first found (unexcavated) and rendered in the standard isometric convention. Stelae and altars are drawn as conventional rectangles and circles, respectively (modified from Healy et al. 2007:19). characterized by a scatter of small housemounds, typically located on hilltops or elevated ridges, perhaps in order to maximize the use of fertile lands for agriculture (Richie 1990; Sunahara 1995:132–133; Healy et al. 2007). Most structures were probably residential in nature, but some may have been used for small-scale craft production, storage, or as kitchens (Richie 1990:199; Sunahara 1995:103; Healy et al. 2004b). 3.2 Archaeological investigations The first reference to the site of Pacbitun is attributed to D. H. Snow (1969), an ethnologist conducting research in San Antonio, who mentioned the presence of 36 Figure 3.5 Core zone of Pacbitun, indicated by dashed lines. Core zone mounds are rendered as black-shaded forms. Possible reservoirs are represented by gray-shaded circular areas (Healy et al. 2007:27). prehistoric mounds and a large pyramidal structure—presumably Structure 1—near the village. In 1971, the site came to the attention of the Department of Archaeology of Belize (then British Honduras) when Structure 41 was quarried for the construction of a modern roadway. Peter Schmidt, then Archaeology Commissioner, conducted a preliminary survey and officially designated the site as “Pacbitun,” which translates to 37 “stones set in earth.” The name might refer to the standing stelae in Plaza A (Healy 1990a). A surface survey was conducted in 1980 by Paul F. Healy. This work showed the presence of numerous well-preserved architectural structures and a widely terraced periphery. Systematic archaeological excavations were first conducted at Pacbitun in 1984, 1986 and 1987 by the Trent University-Pacbitun Archaeological Project, directed by Healy. The aim of the project was to provide a comprehensive perspective on the ancient occupation of Pacbitun by documenting the diachronic development of the site, both in the site core and its periphery (Healy 1990a). Excavations in the epicenter exposed the different architectural phases of constructions, including those relevant to Structures 1, 2, 4, 5, 14, 15, and 23 (Bill 1987; Healy 1988, 1990a, 1992; Healy et al. 2004a; Healy et al. 2004b). The survey of the core zone focused on an area of 1 km2 around the epicenter (Campbell-Trithart 1990), while four transect zones extending 1 km from the epicenter mapped the housemounds located in the periphery zone (Richie 1990; Sunahara 1995). Excavations were also conducted from 1995 to 1997 by the Trent UniversityPreclassic Maya Project in Plazas B, C, and D (Arendt et al. 1996; Hohmann and Powis 1996, 1999; Hohmann et al. 1999). This project aimed to document the Preclassic occupations at the site, with a focus on the organization, social structure, subsistence, and economy of Middle Preclassic domestic households (Healy and Awe 1995a, 1995b, 1996; Healy 1999c). The research also examined the evidence for specialized shell production and its role in the development of socioeconomic complexity in the Belize River Valley (Hohmann and Powis 1996, 1999; Hohmann et al. 1999; Hohmann 2002). 38 Since 2008, new excavations in Plazas A and B were performed by the Pacbitun Regional Archaeological Project (PRAP), under the direction of Terry G. Powis (Powis 2009, 2010, 2011). This project focuses on documenting the earliest occupations at Pacbitun. In addition, PRAP also investigates caves, causeways, and minor centres in the southern periphery of Pacbitun (Powis 2010; Spenard 2011; Valdez et al. 2011; Weber 2011; Weber and Powis 2011; Powis 2012). This new research program seeks to define the extent of settlement around the site and to document the interactions between Pacbitun and its periphery (Powis 2010:23). During the 1995–1997 and 2008–2011 field seasons, excavations were conducted by trowel and shovel, following the cultural stratigraphy. Artifacts were recovered from both primary (floor and perimeter deposits) and secondary (construction fill, structural fill, and secondary middens) contexts. Particular attention was given to the excavation of Plaza B sub-structures in 2008–2010. Floor deposits were excavated according to 5 cm intervals in order to control for the recovery of artifacts embedded in the floor surface. Any artifacts found below the initial 5 cm depth were considered as secondary fill rather than primary floor deposits. During the excavations, visible artifacts were collected by hand and all deposits were dry-screened in the field using a 1/4 inch (6 mm) wire mesh screen. Additionally, in 2008 and 2009, all the floor deposits from Sub-Structures B-1 and B-2 in Plaza B were wet-screened with the use of 1/16 inch (1.2 mm) mesh screen (Powis 2009:18–20). 3.3 Site chronology Excavations at Pacbitun have revealed a long sequence of occupations extending from the early Middle Preclassic (ca. 900 BC) to the Terminal Classic (ca. AD 900) 39 periods (Healy 1990a). The cultural history was first established by cross-dating ceramics with cultural sequences already established for other sites in the Belize Valley (Figure 3.6), specifically Barton Ramie (Gifford 1976) and Cahal Pech (Awe 1992). The chronology was then tested with 22 radiocarbon dates (Healy 1990a, 1999b; Healy et al. 2004b). Additional radiocarbon dates obtained by PRAP also helped to refine the chronology for the Middle Preclassic occupations (Powis 2009). Figure 3.6 Chronology and ceramic complexes of Pacbitun in comparison to those of Barton Ramie, Xunantunich, and Cahal Pech (Healy et al. 2007:21). To this date, there has been no secured evidence that Pacbitun was permanently or densely occupied before the Middle Preclassic (900–300 BC). This time period is locally 40 referred to as the Mai phase and is subdivided into early and late periods at ca. 650 BC. Pacbitun was then a small farming village, relying on swidden agriculture (Wiesen and Lentz 1999) and involved in the manufacture of shell ornaments (Hohmann 2002; Powis 2009, 2010). The village was likely confined to the epicenter given that surveys of housemounds in the core and periphery zones failed to find evidence of clear Middle Preclassic occupation (Sunahara 1995:108; Healy et al. 2007). Because the Middle Preclassic is the focus of the present study, this period is discussed in greater details in sections 3.4–3.6. The Late Preclassic Puc (300–100 BC) and Terminal Classic Ku (100 BC – AD 300) phases witnessed the construction of the first monumental architecture in the site core. The major buildings in Plaza A formed an E-Group complex, which consisted of a standard trio of temple-pyramids (Structures 1, 4 and 5) opposing a lone temple-pyramid (Structure 2) (Figure 3.4). Plazas A and E were plastered during this time period and a ceremonial ballcourt (Structures 14 and 15) was also constructed (Healy 1990a, 1992; Healy et al. 2004b). The presence of E-Groups and ballcourts at Pacbitun likely reflects an early involvement in ceremonial activities at the site (Healy 1990a, 1992). Importantly, it is during this time period that the core zone and the periphery were first settled by small groups (Campbell-Trithart 1990:313; Richie 1990:194–195; Sunahara 1995:100; Healy et al. 2007). During the Early Classic Tzul phase (AD 300–550), many major public structures were enlarged (e.g., Structures 1, 2, 4, 5, 14, and 15), while others, such as elite residences (Str. 23 and 38), were constructed (Healy 1990a; Cheong 2013). Elite individuals were interred with substantial quantities of exotic goods (Bill 1987; Healy 1990a). New monuments were erected, including a carved stela (Stela 6) portraying the 41 accession to the throne of a Pacbitun lord around AD 485. This stela is one of the earliest dated monuments in the southern Maya lowlands (Healy 1990b; Helmke et al. 2006). All these activities attest to the increasing wealth of the site and suggest that Pacbitun was already playing a dominant role in the eastern region of the southern lowlands during this period (Healy et al. 2004b). The developmental peak of Pacbitun occurred during the Late Classic Coc phase (AD 550–700). Almost every building in the epicenter underwent massive architectural renewal at this time (P.F. Healy, 2013, personal communication). Large stone monuments were carved and erected. Fine local or imported objects were frequently deposited as offerings in elite burials (Healy 1988, 1990a; Healy et al. 2004a). The population is believed to have peaked during the Late to Terminal Classic period, with an estimate of 5000–7000 persons living within an area of 9 km2. This coincided with an unprecedented period of agricultural intensification, resulting in the widespread use of hillslope terracing (Campbell-Trithart 1990:317–318; Richie 1990:194–197; Healy 1990a; White et al. 1993; Sunahara 1995:114–116; Healy et al. 2007). The periphery was extensively occupied during this time period (Richie 1990:198–199; Sunahara 1995:100). The site continued to grow and expand during the Terminal Classic Tzib phase (AD 700–900), although on a smaller scale, before it started to decline. Pacbitun was abandoned around AD 900. There is little evidence of activity during the subsequent Postclassic period (Richie 1990:194; Healy 1990a). 3.4 Middle Preclassic investigations Given that the faunal remains discussed in this study were recovered exclusively from Mai phase deposits, more information is provided about the Middle Preclassic 42 architectural and artifactual findings of the 1995–1997 and 2008–2011 excavations at Plaza A, B, C, and D (Figure 3.4). The earliest architectural remains of Plaza B date to the early Middle Preclassic (900–650 BC) and consist of two partially exposed platforms (Sub-Structures B-1 and B4) and a wall (Sub-Stone Alignment B-12) lying about 10–15 centimeters above the bedrock (Figure 3.7). The structures were modest, consisting of low platforms with retaining walls formed of two courses of roughly-shaped limestone blocks. The presence of postholes in the decomposed bedrock suggests that the platforms supported perishable superstructures (Hohmann and Powis 1996, 1999; Hohmann et al. 1999). These platforms are the earliest constructed at Plaza B and, perhaps, at Pacbitun. Two radiocarbon samples collected from Sub-Str. B-1 provided an age of 815–530 BC and 760–410 BC3. Those dates are consistent with the ceramic typology (Healy 1999b; T. G. Powis, personal communication, 2012). Some changes occurred during the late Middle Preclassic (650–300 BC). Sub-Strs. B-1 and B-4 were abandoned around 650 BC and partially covered over, providing a stable foundation for the construction of eleven new platforms (Sub-Strs. B-2, 3, 5–11, 13, and 14). Radiocarbon samples retrieved from Sub-Strs. B-2 and B-3 provided date ranges of 770–375 BC and 905–400 BC, respectively (Healy 1999b). The newer platforms were better constructed and larger than previous phases of construction, with walls made of three courses of cut limestone blocks (Hohmann and Powis 1996). The close proximity of the platforms and common extramural areas suggest that the structures were organized as a patio group with several platforms situated around an open plaza. 3 All radiocarbon dates provided in this study are calibrated and presented with two sigma deviations. 43 Figure 3.7 Plan of the Middle Preclassic sub-structures in Plaza B. The early Middle Preclassic structures are shaded in black (Hohmann et al. 1999:22). This is a common residential pattern observed at many lowland Maya sites (McKillop 2004a:150; Powis 2010:11). While each of the buildings may have served a distinct function, such as kitchens, storage areas, or residences, the presence of substantial quantities of domestic refuse both within and around the structures suggest that they were principally domestic households (Hohmann and Powis 1999; Powis 2010). Sometime during the late Middle Preclassic, the late Mai sub-structures were abandoned and covered with a dense, midden-like deposit. The midden is characterized by a dark organic soil with significant quantities of artifacts and ecofacts. Because it was 44 not found in association with architectural features, it has been inferred that the midden was made from materials derived from other areas of the site and used as construction fill to level and possibly enlarge the plaza (Hohmann and Powis 1999). A radiocarbon sample provided a date range of 780–395 BC for this construction (Healy 1999b), whereas the ceramic typology indicates that it was likely deposited closer to the end of the late Mai phase, ca. 400–300 BC (Hohmann and Powis 1996). Despite the discrepancy in the age estimates, both sets of dates fall within the late Middle Preclassic period. Excavations in Plaza A have exposed an alignment dating from the transitional period (300–100 BC) between the late Middle Preclassic and early Late Preclassic. Located in front of Str. 4, this wall made of cut limestone possibly forms the edge of a platform, but further excavations are needed to determine its size and function. The modes of construction of this sub-structure are very similar to the sub-structures found in Plaza B (T. G. Powis, personal communication, 2012). In the center of the plaza, a retaining wall (Sub-Str. A-1) was also uncovered (Figure 3.8). Ceramics found outside of the structure, below a plaza floor, provided a late Middle Preclassic date (400–200 BC) for this construction. Below this floor, three additional sealed plaza floors (Levels 6–8) were uncovered. An early Middle Preclassic occupation was confirmed by a radiocarbon sample from Level 8 (which provided a date range of 700–400 BC) and the ceramic typology. Four plaza floors with a comparable chronology were also observed inside SubStr. A-1 (Powis 2011; T. G. Powis, personal communication, 2012). The chronology for Plaza A shows the same temporal sequence identified in Plaza B (T. G. Powis, personal communication, 2012) and on the adjacent Eastern Court (Cheong 2013). Excavations in Plaza C have revealed the presence of two early Mai (Sub-Str. C-2 and C-3) and two late Mai structures (Sub-Str. C-1 and C-4) (Arendt et al. 1996; 45 Hohmann et al. 1999; Hohmann 2002:191). Two additional Middle Preclassic stone alignments were uncovered on the western slope of Plaza C (Hohmann et al. 1999). These structures are all similar to those uncovered in Plaza B, although no alleyway or perimeter deposit were encountered (Hohmann 2002:191). A cist burial (BU-C1) dating to the Middle Preclassic was also identified. The interment included a 30–40 years old individual lying in a prone position, with the head oriented to the west. The cist contained one mano fragment, two shell disk beads, one obsidian blade fragment, and three simple vessels (Arendt et al. 1996; Healy et al. 2004b). Figure 3.8 Plan of the Middle Preclassic Sub-Structure A-1 in Plaza A. Image courtesy of PRAP. 46 A small test unit in Plaza D exposed a total of five marl floors and four stone alignments (Sub-Stone Alignments D-1, 2, 3, and 4). The earliest stone alignment dates to the transition from the early to late Middle Preclassic, ca. 650–600 BC. The three others date to the late Middle Preclassic. Artifacts were sparse (Hohmann et al. 1999). 3.5 Artifactual assemblages from the Middle Preclassic period The artifacts recovered at Pacbitun are numerous and diverse. Local materials include granite, slate, and chert (Table 3.1). These could be quarried from sources in the Belize River Valley as well as the Mountain Pine Ridge (Figure 3.2) (Graham 1987; Healy et al. 1995; Hohmann and Powis 1996). Three types of Preclassic artifacts were acquired through long-distance trade: obsidian, jade, and marine shell (Table 3.1). Physiochemical analysis of 18 Middle Preclassic obsidian specimens demonstrated that the volcanic glass was imported from three highland Guatemalan sources (Healy 1990a; Awe et al. 1996; Hohmann and Powis 1996:118–119), while the greenstone and jade possibly came from the Motagua River Valley of Guatemala (Healy 1990a; Hohmann and Powis 1996). Marine shells were imported whole from the Caribbean coast and used in the manufacture of shell ornaments. A small proportion of the artifacts were also made from local freshwater species, namely the pearly mussel and the locally available jute (Hohmann 2002:115–117; Powis 2009, 2010). The majority of the shells were transformed into small disks and irregular beads (Hohmann 2002:125). Evidence suggests that the early Maya of Pacbitun were involved in the specialized production of shell ornaments at the household level. The majority of ornaments were likely destined for 47 export to other Maya sites, likely into the Petén region of Guatemala (Hohmann 2002:192–194; Powis 2009). Table 3.1 Possible source location for local and exotic raw materials found at Pacbitun. Artifact types Granite Local/Exotic Local Possible sources Stann Creek Macal River Mountain Pine Ridge Distance 5–10 km Slate Local Slate Creek Little Vaquero Creek Barton Creek 5–10 km Chert/Chalcedony Local Belize River Valley 10–20 km Marine shell Exotic Caribbean coast ~100 km Jade/Greenstone Exotic Motagua River Valley ~150 km Obsidian Exotic El Chayal San Martin Jilotepeque Ixtepeque 400–500 km Temporal changes in the quantity and quality of artifacts recovered from the substructures suggest subtle social and economic differences during the Middle Preclassic (Arendt et al. 1996; Hohmann and Powis 1996, 1999; Hohmann et al. 1999; Powis 2009, 2010). The artifacts indicate that the Pacbitun inhabitants were essentially egalitarian during the early Middle Preclassic. During the late Middle Preclassic, the social system may have become gradually hierarchical, as indicated by the higher frequency and greater diversity of long-distance exchange goods and the presence of substantial quantities of shell ornaments. There are also signs of a greater degree of standardization in the production of artifacts, such as disk shell beads (Hohmann 2002). 48 3.6 Subsistence practices As discussed in Chapter 2, it is believed that the Preclassic Maya subsisted primarily on the cultivation of three cultigens: maize, beans, and squash (Turner and Miksicek 1984; Lentz 1999; Lentz et al. 2005). Unfortunately, evidence for agriculture during the Middle Preclassic is scarce at Pacbitun, perhaps as a result of poor organic preservation. Few preserved kernel cupules of maize were identified in two late Middle Preclassic samples (Wiesen and Lentz 1999), but no paleobotanical remains of beans or squash were recovered. The recovery of multiple fragments of grinding tools, such as mano and metate, may constitute indirect evidence for the consumption of wild and domesticated plants, including maize (Hohmann and Powis 1996; Duffy 2011). Remains of the coyol palm, “turtlebone” (Pithecolobium sp.), and ramón have also been identified (Wiesen and Lentz 1999). Wiesen and Lentz (1999) suggest that the residents of Pacbitun possibly exploited these plants for various usages, such as food, medicine, artifact manufacturing, construction materials, and fuel. Faunal remains recovered from Preclassic contexts during the 1995 and 1996 excavations in Plaza B and C were previously analyzed by Norbert Stanchly (1999). The preliminary report provided NISP counts (Table 3.2). MNI values were not calculated. According to Stanchly (1999), a total of 2,327 specimens were recovered, with 1,575 invertebrate remains (67.7% of the assemblage) and 752 vertebrate remains (32.3%). Freshwater molluscs include jute snails, apple snails, and pearly mussels. More than 100,000 jute remains were recovered between 1995 and 1997 from Plaza B investigations. From this, 225 jute were selected for analysis. All specimens presented a broken apex or punctured spire. Both methods are believed to facilitate the detachment of the snail from the shell after it is cooked (Healy et al. 1990; Stanchly 1999). Based on the 49 Table 3.2 Vertebrate and invertebrate remains identified by Stanchly (modified from Stanchly 1999:49–50). VERTEBRATES Taxon Osteichthyes Ictaluridae Unidentified fish Aves Bird? Unidentified bird Reptilia Chelonia? Chelonia Kinosternon spp. Staurotypus triporcatus? Unidentified reptile Mammalia Dasypus novemcinctus Dasypus novemcinctus? Sylvilagus sp. Sylvilagus sp.? Tapirus bairdii Carnivora Canis lupus familiaris Canis lupus familiaris? Cervidae Cervidae? Odocoileus virginianus Mazama americana Tayassuidae Rodentia Rodentia? Cuniculus paca Cuniculus paca? Homo sapiens Unidentified mammal Unidentified specimens Total n 1 1 12 1 6 3 14 1 2 12 1 1 1 1 1 1 2 66 29 53 3 4 1 1 5 1 4 434 90 752 INVERTEBRATES Taxon Gastropoda Strombus pugilis Strombus sp. Strombus sp.? Pachychilus indiorum Pachychilus glaphyrus Pachychilus sp. Pachychilus sp.? Pomacea flagellata Pomacea sp.? Prunum apicinum Orthalicus sp.? Olividae Neritida Pelecypoda Nephronaias ortmanni Donax sp. Chamidae Arcinella sp. Scaphopoda Dentalium sp. Mollusca Unidentified shell Total n 2 565 4 158 64 3 1 24 4 12 1 1 1 725 1 1 1 1 5 1575 extremely large numbers of jute recovered at Pacbitun in fill and midden contexts, Healy and colleagues (1990), as well as Stanchly (1999), suggested that the freshwater snail possibly played a significant role in the subsistence of the Preclassic Maya. However, more recent analyses by Solis (2011) indicate that natural processes and rodent activity 50 may alter the shells in a fashion identical to the patterns created by cultural activities. Therefore, broken spires may not necessarily be indicative of human consumption of jute, as frequently argued in the Maya literature. Solis (2011) suggested instead that the presence of jute in Terminal Preclassic deposits at the site of Minanha is more likely due to the incidental inclusion of jute in river clays used as construction fill. A re-examination of the archaeological contexts and artifacts associated with the Pachychilus remains could help to determine the use of these snails at Pacbitun. Similarly, the importance of apple snails and pearly mussels to the diet is poorly understood (Stanchly 1999). Powis (2004) has suggested that freshwater mussels possibly served as a dietary supplement or famine food when other protein sources were unavailable. Marine molluscs, which were used for the manufacture of shell ornaments, may also have been imported from the coast as a source of food, the meat being salted or smoked (McKillop 2004b). However, data is currently lacking to test these hypotheses. Of the 752 vertebrate remains from Plaza B and C, 224 were identified below class level by Stanchly (1999). Mammalian species include white-tailed deer, red brocket deer, paca, rabbit, armadillo, domestic dog, peccary, and tapir. Turtle remains are represented by shell fragments of small mud turtles and possibly the giant Mexican musk turtle. Fish remains include one catfish element. Bird remains are also present, but are too fragmented to be identified below class level. The size of the fragments suggests the presence of a medium to large bird. All of these vertebrate species were probably consumed as subsistence items. Deer specimens dominate the assemblage. The unidentified mammalian fragments are consistent with this picture (Stanchly 1999). Stanchly suggests that the Preclassic Maya of Pacbitun hunted both small and large terrestrial game and gathered turtles and shellfish. Most of the animals could have been 51 obtained from local ecozones. The wide spectrum of species exploited, despite the small sample of the assemblage, is typical of lowland Maya faunas (Stanchly 1999). 3.7 The Middle Preclassic at Pacbitun: A summary During the Middle Preclassic period, which is the focus of this research, Pacbitun was a small farming village consisting of a dispersed scatter of households, as evidenced by the presence of sub-plaza structures in the epicenter. Indeed, the various programs of excavations revealed that the Middle Preclassic settlement extended to portions of at least four plazas (A, B, C, and D), covering an area of 300 m (east-west) by 125 m (northsouth). There seems to be no evidence of Middle Preclassic settlement outside the epicenter based on the extant data. Healy and colleagues (2007) have estimated a population of 16–49 persons, but this value is likely underestimated because it only takes into account the structures uncovered in Plaza B. The various classes of artifacts recovered within and around the structures (e.g., ceramics, jade and shell ornaments, lithics tools) all indicate that the Middle Preclassic residents of Pacbitun were involved in typical household activities, such as food preparation and tool manufacture. The presence of exotic goods, such as obsidian, jade, and marine shells, confirms that Pacbitun was participating in inter-regional exchange systems at an early date. The preliminary paleobotanical and archaeozoological data suggest that the Pacbitun Maya practiced swidden agriculture, which they may have supplemented with the hunting and gathering of an array of locally available animals and plants. This chapter has presented the geographical context and cultural history of Pacbitun as well as detailed the archaeological investigations undertaken at the site. This 52 background information will be necessary to an interpretation of the Pacbitun faunal material (Chapter 7). The following chapter turns to the theoretical framework used to analyze this material. 53 CHAPTER 4: FORAGING THEORY The theoretical approach guiding this research is foraging theory. This chapter defines and examines three types of foraging models used in archaeozoology: the prey choice model, patch choice model, and central place foraging model. After presenting the assumptions and predictions of each model, this chapter considers how the central place foraging prey choice model is most appropriate for interpreting faunal assemblages at Pacbitun. It also discusses how foraging theory can be applied to the archaeological record. The second part of the chapter offers a description of the ecology and behavior of the species identified at Pacbitun. 4.1 Theoretical approach Foraging theory is a family of models derived from human behavioral ecology. Central to this theoretical framework is the premise that foraging behaviors are under selection and contribute to enhance an individual’s chances of survival and reproductive success (Smith 1983; Bird and O'Connell 2006). Specifically, in anthropology, it is assumed that foragers were concerned with maximizing their net rate of energy acquisition under a certain set of environmental conditions. This approach is commonly applied to the study of subsistence strategies, transport decisions, and technological changes (Bird and O'Connell 2006). The following section discusses three fundamental sets of foraging models used in archaeozoology to examine the decisions underlying the acquisition of animal resources. 54 4.1.1 Prey choice model The prey choice model, also known as the diet breadth model, aims to predict which resources a forager should include in its diet or ignore. When foragers encounter prey, they have to decide whether they should exploit it or continue searching for a more profitable one (Smith 1983; Stephens and Krebs 1986). The prey choice model assumes a “fine-grained” environment; that is, an environment within which prey are randomly distributed (MacArthur and Pianka 1966; Smith 1983). The model further postulates that a forager searches for all types of prey simultaneously and encounters them sequentially in the environment (MacArthur and Pianka 1966; Stephens and Krebs 1986; Bird and O'Connell 2006; Lupo 2007). Foraging time is divided into two mutually exclusive activities: searching and handling. Searching is defined as the time devoted to looking for resources. Handling consists of the time spent pursuing, capturing, processing, and consuming a prey item that has been encountered (MacArthur and Pianka 1966; Smith 1983; Stephens and Krebs 1986; Bird and O'Connell 2006; Lupo 2007). The model postulates that foragers can accurately estimate the likely encounter and post-encounter return rate for all potential prey types because they possess prior information about the abundance of resources in a habitat and the costs and benefits associated with their acquisition (Stephens and Krebs 1986). The prey choice model requires resources to be ranked as a function of their “profitability”, which is measured as the net post-encounter return rate (Smith 1983; Stephens and Krebs 1986; Bird and O'Connell 2006; Lupo 2007). According to the model, prey types are added to—or deleted from—the diet as a function of their rank order so that the overall foraging return rate is maximized (Smith 1983; Stephens and Krebs 1986; Bird and O'Connell 2006; Lupo 2007). As a result, foragers are expected to 55 always pursue the highest-ranked prey type whenever encountered because this strategy provides the highest net gain of energy per unit of handling time (Smith 1983; Bird and O'Connell 2006; Lupo 2007). Less profitable prey types, regardless of their abundance in the environment, should be included in or excluded from the diet depending on the probability of encountering higher-ranked resources. In fact, low-return prey taxa should always be ignored if their acquisition does not result in an increase of the overall foraging return rate (Smith 1983; Stephens and Krebs 1986). Given these predictions, variations in diet breadth (i.e., number of prey types exploited) can be used to assess foraging efficiency. In a rich environment, foragers should have a narrow diet dominated by a relatively small number of prey types. However, if the availability of highly profitable resources declines substantially, either through predation or environmental change, foragers may be forced to handle an increasing number of less profitable prey types. This situation should progressively produce a broader diet (Smith 1983). The prey choice model postulates that prey types are found in a fine-grained environment. However, this assumption is violated when resources are clumped together, that is, when they form “patches.” The patch choice model, which is discussed next, represents a useful alternative in this situation. 4.1.2 Patch choice models First developed by MacArthur and Pianka (1966) as a complement to the prey choice model, the patch choice model predicts foraging behaviors in environments where resources occur in patches (Smith 1983). Patches are assumed to be distant from one another and the time spent travelling from one patch to another is considered 56 unproductive (Stephens and Krebs 1986). Two mutually exclusive activities are defined by the model: travelling and handling (MacArthur and Pianka 1966; Lupo 2007). The patch choice model presumes that patches are encountered randomly and sequentially in the environment and are ranked according to their respective profitability (MacArthur and Pianka 1966; Stephens and Krebs 1986). Ranks are established as a function of the return rate expected from searching for and handling prey types within each patch, while taking into account the cost of travelling to them (Bird and O'Connell 2006). Overall, the model predicts that foragers add patches to their itinerary in rank order until the average foraging return per unit (including travelling) declines (Smith 1983; Lupo 2007). Although the patch choice model is designed to determine which patches foragers should exploit, it does not consider time allocation within these patches. The marginal value theorem proposed by Charnov (1976) acts as a natural extension to the patch choice model and focuses on explaining these issues (Smith 1983; Stephens and Krebs 1986). At the heart of the model is the assumption that foraging generally depletes a patch from its resources (Charnov 1976). As a forager spends more time in a patch, highly-ranked prey normally become rarer; the energy cost of searching for resources gradually increases, which results in a steady decline of the marginal return rate of that particular patch (Smith 1983; Winterhalder and Kennett 2006; Lupo 2007). As a consequence, the marginal value theorem predicts that a forager should leave a patch when travelling to and exploiting another patch yields higher return rates (Smith 1983; Bird and O'Connell 2006; Winterhalder and Kennett 2006; Lupo 2007). A central assumption of the model is that the optimal time allocation to any patch is a function of the average return rates for all utilized patches. In general, when resources are abundant or when patches are in close proximity to one another, foragers should not spend much time in a patch. However, 57 when food availability declines or when travel time between patches increases, it becomes more profitable to increase time residency (Smith 1983; Stephens and Krebs 1986). Ultimately, patches will be ignored unless their marginal return rate equals to or is greater than the average rate for the utilized set of patches (Smith 1983; Lupo 2007). The previous models assume that foragers consume prey at the point of capture. However, foragers may preferentially transport resources to a central place for consumption or provisioning (Orians and Pearson 1979; Cannon 2003). This issue is addressed by central place foraging models. 4.1.3 Central place forager prey choice model Central place foraging (CPF) models (e.g., Orians and Pearson 1979; Schoener 1979) are designed to examine how travel and transport costs influence foraging decisions regarding prey choice, load size, patch selection, and patch time allocation (Lupo 2007). Following the assumption that the goal of foragers is to maximize their net rate of energy delivery to a central place, these models seek to predict which prey types foragers should transport and how their decisions vary as a function of the distance from a central place (Orians and Pearson 1979). However, most CPF models do not take into account how the processing of resources at their location of acquisition can increase the utility of a load. Small prey items may not need to be processed. In contrast, when foragers capture large prey, they often need to decide which parts to bring home and which ones to leave behind so as to maximize the net delivery rate (e.g., Metcalfe and Barlow 1992; Bird and Bliege Bird 1997; Cannon 2000, 2003; Bird and O'Connell 2006). Cannon’s (2003) central place forager prey choice model is designed to predict foraging decisions regarding prey selection and field processing for foragers who travel 58 from and to a central place, taking into account that there is a maximum load size that can be transported. Similar to the prey choice model, the CPF prey choice model ranks prey types in decreasing order as a function of their profitability. However, unlike the former which only considers post-encounter return rates for ranking prey types, the latter also takes into consideration search, travel, and, when it applies, field-processing costs to estimate the utility of prey types (Cannon 2003). Because search costs are included in the calculation of delivery rates, a taxon ranked high when abundant near the site is considered of lower value when found in distant patches. Additionally, the CPF prey choice model does not assume that all resources are searched for simultaneously. On the contrary, Cannon (2003) indicates that central place foragers often leave on foraging trips with a specific resource in mind, even though they might come back with a different one. Furthermore, the model does not presume that resources are clumped in space, although it is compatible with the presence of patches in the environment (Cannon 2003). In Cannon’s model, the relationship between processing time and load utility is assumed to approximate a diminishing-returns function (Cannon 2003). When search or transport costs increase, foragers should invest more time in field-processing large-bodied prey taxa in order to maximize the net delivery of food to the central place (Cannon 2003). Consequently, the analysis of skeletal part representation may provide information on past foraging strategies. Skeletal profiles reflecting low average search times should include a wide range of parts, including low-utility portions, while higher average search times should result in assemblages heavily dominated by highly-ranked portions. If the goal of central place foragers is to maximize the net rate of energy delivery, these foragers should select the prey types that provide the highest delivery rates. Considering equivalent search, transport, and field processing times, large prey types (i.e., 59 high-ranked prey) should be more profitable than small-sized animals (Cannon 2003). However, if the abundance of highly profitable prey taxa in patches near the camp declines, the cost associated with their acquisition increases. In this situation, an initially high-ranked taxon may become a new, lower-ranked prey type if it must be acquired in a remote location. The CPF prey choice model predicts that, at this point, foragers may concentrate their efforts on the procurement of lower-ranked, smaller-sized resources that are abundant near the residential site (Cannon 2003). However, if the search and transport costs of the small taxa increase as well near the site, foragers should increase their net delivery rate by focusing on high-ranked resources located in distant patches. This prediction of the CPF prey choice model implies that an increase in the abundance of large prey types relative to smaller ones, combined with an increase in field-processing intensity, may signal decreased rather than increased foraging efficiency (Cannon 2003). 4.2 Archaeological applications of foraging theory 4.2.1 Use of foraging models in this study Foraging models are commonly used in archaeology to make predictions about foraging behaviours and to test hypotheses about resource depression and foraging intensification. The models are most frequently used to assess changes in foraging efficiency on the long term (Bird and O'Connell 2006; Lupo 2007). However, such application may be limited at Pacbitun. Although the faunal material was recovered from two distinct occupations (i.e., early Middle Preclassic and late Middle Preclassic), small sample size may require the assemblages to be combined, which prevents temporal comparisons between the two phases of the Middle Preclassic period. Given that the Maya were sedentary farmers, the CPF prey choice model was selected to investigate the 60 exploitation of animal resources at Pacbitun. In accordance with Cannon’s model, the diet breadth at Pacbitun will be characterized through the use of prey ranking and abundance indices (see below). Foraging efficiency and acquisition of resources will also be examined through a consideration of transport decisions. 4.2.2 Prey rankings Applications of foraging theory to archaeology must start with the ranking of prey types. Traditionally, prey body size has been used as a proxy for estimating the net return rate of resources (e.g., Broughton 1994; Cannon 2003; Broughton et al. 2011). In these studies, the relationship between body size and profitability is assumed to be curvilinear. Very small prey types, such as mice, and very large animals, such as whales, are not considered as profitable as prey of intermediate sizes because a considerable amount of energy must be invested in handling them. Between the two extremes, it is generally considered that profitability increases with body size; large prey animals (e.g., deer and tapir) are ranked higher than smaller animals such as rabbits or agoutis (Broughton 1994). Hunting technology may, however, impact return rates. For instance, the profitability of some small animals, such as rabbits, may be increased if these are collected en masse (Jones 2006); this situation would be in contradiction with the body size because it alters the relationship between prey body size and energetic return rates. Additionally, gregarious species may be considered more profitable than solitary ones because many individuals may be handled in one foraging bout. In the Pacbitun assemblages, such animals would be the peccary and coati (see section 4.3). The use of the prey body size as a proxy for prey profitability also fails to take into account the impact of prey mobility on return rates. Indeed, high prey velocity should 61 result in decreasing probability of capture (Stiner et al. 2000; Bird et al. 2009; Bird et al. 2012). In order to examine this issue, Morin (2012) compared the body mass and maximum running speed of a broad range of mammals. He concluded that the body size rule works best for mammalian taxa within the size range of 50–700 kg. Unfortunately, most mammals inhabiting tropical forests, with the exception of the tapir and jaguar, weigh less than 50 kg. For these last species, rankings based on body size can be confounded by differences in prey mobility and predatory defense mechanisms (Stiner et al. 2000; Bird et al. 2009; Bird et al. 2012). Sessile and slow-moving animals using carapaces or quills (e.g., molluscs, tortoise, porcupine) to deter predators are generally associated with lower pursuit costs and higher chances of capture than animals of similar body weight (e.g., agouti, rabbit) that escape at great speed (Stiner et al. 2000; Bird et al. 2009; Morin 2012). This situation result in a violation of the body size rule if a smallsized animal was to be found to be more profitable than a larger one. This seems to be the case in Australia where Bird and colleagues (2009; 2012) suggest that prey mobility is often a better criterion for estimating the likelihood of capturing small prey items (<25 kg) than body mass. Morin (2012) suggests that, when prey types are well-separated from one another in term of body size, overlap in return rates and, therefore, rank inversions are less likely. To test this hypothesis, he compared the net return rates and body masses of faunas from different latitudinal environments. He observed that the body size rule is stronger in cooler habitats where faunal communities are comprised of several large-sized taxa of variable body weights. This implies that the body size rule may not be the most robust measure of profitability for tropical environments where faunas are generally characterized by a narrow range of similarly-sized animals. Concerning this issue, 62 Broughton and colleagues (2011) argue that when two taxa are well-separated in body size and are considered of similar mobility (e.g., “fast” prey such as hare vs. deer), the larger taxon should provide a higher return rate than the small prey type in accordance with the body size rule (Broughton et al. 2011). However, prey mobility may have a stronger impact on prey rankings and cause rank inversions when the faunal data set only includes a very narrow range of small-bodied prey (<30 kg). The construction of prey rankings at Pacbitun was established using body mass as a proxy for net return rates. However, as a result of the above concerns, interpretations of the results at the site will need to consider the issue of mobility, en masse collection, and gregariousness of certain species. Body weights of mammalian taxa were obtained from Emmons (1997) and Reid (2009) (Table 4.1 and Figure 4.1). Although carnivores were likely procured by the Maya for raw materials (e.g., pelt, teeth, and long bone shafts) or ritual purposes (Pohl 1983; Hopkins 1992; Emery 2010), they could also have been consumed. Therefore, they were included in the rankings for comparisons with other taxa. The tapir would have been the highest-ranked species by a considerable margin, followed by a group of highly-ranked prey taxa comprised of large felines (i.e., jaguar and puma) and artiodactyls (i.e., white-tailed deer, white-lipped peccary, red brocket deer, and collared peccary). The ocelot, paca, margay, nine-banded armadillo, coati, and agouti form a second group of intermediate sizes (3–10 kg). Four animals, the opossum, rabbit, pocket gopher, and long-tailed weasel, occupy the lowest positions on the ranking scale (<3 kg). Turtles were not included in prey ranking because, as slow-moving animals, they possibly were always included in the optimal diet despite their small size (Morin 2012), in violation with the body size rule. Small sample size and limited taxonomic identification made the ranking of fish and bird species impracticable in the present case. 63 Table 4.1 Data and references for body mass of mammalian taxa at Pacbitun. Mass (in kg) 1 180.0 65.0 44.5 34.0 33.5 22.0 19.0 10.8 8.5 5.0 4.6 3.8 3.5 1.5 1.0 0.8 0.5 Common Name Tapir Jaguar Puma White-tailed deer White-lipped peccary Red brocket deer Collared peccary Ocelot Paca Nine-banded armadillo White-nosed coati Margay Agouti Opossums Rabbits Pocket gophers Long-tailed weasel Source Reid (2009) ” ” ” ” ” ” ” ” ” ” ” ” ” ” Emmons (1997) ” Comparative specimens (Didelphis marsupialis) (Sylvilagus brasiliensis) (Orthogeomys hispidus) 1 When a range of weights was available or when values were given separately for males and females, midpoints were used to calculate body mass. Tapir Jaguar Puma White-tailed deer White-lipped peccary Red brocket deer Collared peccary Ocelot Paca Nine-banded armadillo White-nosed coati Margay Agouti Opossums Rabbits Pocket gophers Long-tailed weasel 0 20 40 60 80 100 Mass (in kg) 120 140 160 180 Figure 4.1 Ranking of mammals at Pacbitun according to body mass. Data from Table 4.1. 64 Animal resources may have been procured by the Maya not only for their meat, but also for their fat content. In the Maya subarea, certain animals of intermediate size, such as the agouti, paca, and armadillo, are lean during the dry season, but during the wet season, they can put on layers of fat greater than 2.5 cm in thickness (Hill et al. 1984). This proportion of fat to body weight is extremely high compared to that of the whitetailed deer, whose fat content fluctuates from 2% during the dry season to 10% during the wet season (Hill et al. 1984). This difference in fat content may cause rank inversions if the Maya would have targeted small fatty animals, particularly during the wet season. Unfortunately, it is not possible to test this hypothesis at Pacbitun because of a lack of data. Percentage of fat relative to body weight is difficult to estimate and is not reported for a large number of taxa (Morin 2012). For instance, data on fat percentage to body weight was only found for four mammals in the Pacbitun assemblages, which is not sufficient for ranking prey according to this criterion. 4.2.3 Abundance indices Abundance indices are often used as proxy estimates to interpret variations in the faunal record. Abundance indices generally compare a group of high-ranked prey to a group of lower-ranked taxa, taking the form of Ʃ large taxa / (Ʃ small taxa + Ʃ large taxa) (Morin 2012; Ugan and Simms 2012). These subsets may be established for prey of similar mobility but of different sizes (e.g., leporids versus artiodactyls in Cannon 2003; Broughton et al. 2011) or, inversely, for prey of similar body size, but of different maximum velocity (e.g., tortoises versus hares in Stiner et al. 2000). Grouping prey types into high- and low-return categories limits the problem of rank inversions and strengthens 65 the relationship between return rates and body size. However, the use of these indices is appropriate only if the two subsets are composed of taxa with clear differences in ranking. Errors may arise if animals of similar profitability (e.g., paca vs. agouti) are compared. Abundance indices should also exclude small-bodied taxa that are likely to be collected en masse (Morin 2012). The abundance indices used in this study are presented in greater details in Chapter 7. 4.3 Animal ecology and behavior This section provides a summary of the ecology and behavior of animals recovered in Middle Preclassic deposits at Pacbitun. It serves as a basis for interpreting taxonomic representation and habitat use in subsequent chapters. It should be noted that reliable information on many Neotropical animals is scarce. Often, little is known about the seasonality and reproduction cycle of these animals because of limited research in the lowland Maya region (Ojasti 1996; Emmons 1997; Emery and Brown 2012). The white-tailed deer is one of the largest herbivores found in the tropics. It is ecologically plastic and can live in a wide variety of habitats, such as tropical savannas, and lightly wooded or swampy areas (Ojasti 1996; Emmons 1997; Reid 2009), but is not a rainforest animal (Ojasti 1996; Emmons 1997; Reid 2009). It thrives in mosaic environments and most often resides at the edge of open and covered landscape (Ojasti 1996; Geist 1998). In Belize, the white-tailed deer is often seen in second growth forests and thickets, forest edges, pine savannas, and sometimes in milpas (Méndez 1984). It is tolerant of altered habitats, adapting quickly to changing environments (Ojasti 1996). Active day and night, the white-tailed deer is most often spotted at dawn or dusk when it ventures in open areas to feed (Ojasti 1996; Reid 2009). The white-tailed deer is a 66 browser and selective feeder that concentrates on plants that are easily digested and feeds predominantly on leaves, fruit, nuts, seeds, and legumes (Méndez 1984; Brown 1994; Ojasti 1996; Emmons 1997; Reid 2009). Highly fibrous plants, such as grasses, contribute little to the diet, but may be consumed when herbaceous forage is unavailable (Verme and Ullrey 1984; Kroll 1994; Ojasti 1996). The white-tailed deer may also feed on crops, such as maize, sorghum, and beans (Ojasti 1996). In the tropics, the white-tailed deer lives in small groups of two to six individuals, but it may also be solitary (Ojasti 1996; Emmons 1997; Reid 2009). Family herds occupy permanent small home ranges (Ojasti 1996). Although reproduction of this animal is synchronous in the north, breeding and fawning seasons extend for several months in Central America (Ojasti 1996; Geist 1998). In fact, breeding can take place at any time of the year, but it generally peaks in certain seasons so that fawning does not occur during times of adverse weather (Geist 1994; Hirth 1994; Geist 1998). As a result, peaks in birthing are generally synchronous within a given locality (Hirth 1994; Jacobson 1994; Ojasti 1996). For instance, fawns are born from April to June in the Yucatán and southern Mexico, from January to June in Honduras, and from May to July in Costa Rica (Ojasti 1996). Females generally give birth to one fawn per year (Ojasti 1996). Tropical whitetailed bucks bear branched antlers, but these are smaller in comparison to northern whitetails. Because the antler cycle is irregular in the tropics, males may be encountered in any stage of antler growth (Geist 1998). Antlers are shed every year (Méndez 1984; Geist 1998; Reid 2009). The red brocket deer is a small tropical ungulate adapted to live in forested environments (Reid 2009). Its small size, short antlers, and rounded back allow it to move through dense vegetation (Ojasti 1996; Emmons 1997). As a result, it is not surprising 67 that this animal favors closed, mature forests, although it may occasionally visit small clearings (Emmons 1997; Reid 2009) and cultivated areas (Ojasti 1996; Emmons 1997). This animal primarily feeds on fruit and flowers found in the underbrush, but may also browse in forest clearings (Ojasti 1996; Emmons 1997). The red brocket deer is a solitary and territorial animal; it occupies the same home range year after year (Ojasti 1996). Bucks bear short, spiked antlers (Emmons 1997; Geist 1998; Reid 2009) which may be retained for more than a year but can be shed at any time (Geist 1998). Similar to most tropical mammals, reproduction in brocket deer may take place year-round (Ojasti 1996; Geist 1998). Peaks in birthing occur at specific times of the year in different regions. Fawns are born between September and April in Surinam, whereas the calving season extends from April to August in Chiapas, Mexico (Ojasti 1996). The red brocket deer normally gives birth to a single young (Ojasti 1996; Reid 2009). Morphologically similar to a pig, the white-lipped peccary is a medium-sized ungulate (Mayer and Wetzel 1987). This gregarious animal lives in large herds formed of 40 to 200 individuals of both sexes (Donkin 1985; Mayer and Wetzel 1987; Ojasti 1996; Emmons 1997; Reid 2009). Its preferred habitats are virgin or near-pristine humid tropical forests (Mayer and Wetzel 1987; Emmons 1997; Reid 2009). It generally avoids disturbed habitats and the proximity of humans (Ojasti 1996). This species is considered nomadic; herds travel long distances throughout the tropical forest and do not stay more than a day or two in a particular area (Mayer and Wetzel 1987; Ojasti 1996; Emmons 1997; Reid 2009). It subsists on a mix of fruit, leaves, seeds, roots, and small vertebrates and invertebrates (Donkin 1985; Mayer and Wetzel 1987), and may sometimes exploit crops, such as maize, sweet potatoes, and manioc (Mayer and Wetzel 1987; Reid 2009). It 68 is believed to breed year-round, with females typically giving birth to twins (Mayer and Wetzel 1987; Ojasti 1996; Reid 2009). The collared peccary is smaller than the white-lipped peccary (Ojasti 1996; Reid 2009). It lives in herds composed of about 15 adults and their young (Donkin 1985; Emmons 1997; Reid 2009). The composition of the group is loose and males may occasionally leave the herd to forage alone (Ojasti 1996; Emmons 1997). The collared peccary occupies permanent home ranges (Ojasti 1996; Reid 2009), but is more versatile than the white-lipped peccary. This species can live in both mature and secondary forests and adapts well to disturbed areas (Donkin 1985; Ojasti 1996; Reid 2009). Its diet consists of fruit, seeds, roots, grasses, invertebrates, and small vertebrates (Donkin 1985; Ojasti 1996; Emmons 1997; Reid 2009). This species commonly raids crops (Ojasti 1996; Reid 2009). Like other ungulates in Central America, the collared peccary can breed yearround. The birthing season lasts from July to August in the southern United States and from March to April in Venezuela. Two birth peaks were observed in southern Mexico, the first extending from January to February, the second from September to October (Ojasti 1996). Females give birth to two offspring on average (Reid 2009). The Baird’s tapir is a large perissodactyl. This animal is normally solitary, but family groups composed of a cow and her offspring are sometimes observed (Emmons 1997; Reid 2009). The tapir favors waterside habitats with dense, low vegetation. Nonetheless, it is ecologically plastic and travels extensively throughout the forest to forage (Emmons 1997; Reid 2009). Being a shy animal, the tapir tends to avoid human settlements, but it may occasionally be spotted raiding crops (Reid 2009). The nine-banded armadillo occupies a wide range of primary and secondary habitats, but is most often seen in thickets and areas of dense vegetation (Emmons 1997; 69 Reid 2009). Sedentary, the animal dens in large burrows during the day and feeds at night on insects and small invertebrates. It may occasionally eat berries and other plants (McBee and Baker 1982; Ojasti 1996; Emmons 1997; Reid 2009). Individuals are solitary, but show no tendency toward territoriality (McBee and Baker 1982; Reid 2009). The periodicity and frequency of armadillo reproduction in Central America is unknown. It is believed that the mating season coincides with the onset of rains from May to August (McBee and Baker 1982; Ojasti 1996). The paca is a large rodent that occupies a wide ecological range of forested environments, from mature and secondary forests to riverine habitats and wetlands (Pérez 1992; Ojasti 1996; Emmons 1997; Reid 2009). It may also occupy wooded areas near agricultural zones (Ojasti 1996; Reid 2009). This animal is mainly active at night when it leaves its underground burrow to forage on fruit, seeds, and young plants (Pérez 1992; Ojasti 1996; Reid 2009). Living in monogamous pairs, the paca occupies an exclusive territory (Ojasti 1996; Emmons 1997). Females generally give birth to a single young (Pérez 1992; Reid 2009). They may have one or two litters per year (Pérez 1992; Ojasti 1996). The agouti is another large rodent inhabiting the tropical forests of Central America. Smaller than the paca, the agouti thrives in forested habitats. Because it is fairly tolerant of modified environments, it can also be found near cultivated lands (Ojasti 1996; Emmons 1997; Reid 2009). As a forest-dweller, this small mammal feeds on a wide variety of fruit and seeds, occasionally supplementing its diet with fungi, sprouts, and crops (Ojasti 1996; Emmons 1997; Reid 2009). Agoutis are most active in the morning or the late afternoon (Ojasti 1996; Reid 2009). A breeding pair of agoutis usually occupies a 70 territory of two to three hectares (Ojasti 1996; Reid 2009). They can breed year-round, with two litters a year as a rule (Ojasti 1996; Reid 2009). Pocket gophers are large, rat-like rodents that live in small isolated communities. These animals spend most of their lives underground where they build deep, complex burrow systems (Emmons 1997). They prefer open habitats with well-drained soils, such as agricultural clearings or hilly forested areas. They generally feed on plant parts that grow underground, such as tubers and stems, but they can also pull down aboveground plants from below (Emmons 1997). Two types of rabbits can be found in Central America: the tapiti and the cottontail. Both species are browsers and grazers (Chapman et al. 1980; Emmons 1997). The tapiti is the only type of rabbit that truly resides in mature tropical forests (Emmons 1997). Mainly nocturnal, it commonly forages in habitat edges and agricultural fields, finding shelter in thickets of dense vegetation (Emmons 1997; Reid 2009). In Chiapas, Mexico, this species breeds year-round (Reid 2009). The cottontail prefers to live in open areas, such as savannas, grasslands, and agricultural fields (Reid 2009). Although this animal is solitary, it is not territorial (Chapman et al. 1980; Reid 2009). Females may have five to seven litters per year (Reid 2009). The white-nosed coati preferentially lives in wooded habitats, but it is occasionally seen near savannas or agricultural fields (Gompper 1995; Emmons 1997; Reid 2009). It spends most of its time foraging on the ground, but it may climb in the canopy to forage fruit trees or rest (Gompper 1995; Reid 2009). Adult females and their offspring travel in groups of about 20 individuals, whereas males are usually solitary (Gompper 1995; Emmons 1997; Reid 2009). This animal is omnivorous and feeds on fruit, invertebrates, and small vertebrates (Gompper 1995; Emmons 1997; Reid 2009). In 71 the few populations surveyed, coatis breed synchronously once per year, although the timing of the breeding season differs between regions (Gompper 1995). The long-tailed weasel efficiently occupies a wide range of environments. It can inhabit forested locales but it usually prefers open areas and agricultural lands (Emmons 1997; Reid 2009). This animal is a generalist predator (Sheffield and Thomas 1997). In tropical settings, it preys on small mammals (less than 50 g), rabbits, pocket gophers, birds and their eggs (Sheffield and Thomas 1997; Reid 2009). Out of the den, it is active day and night; most of the time is spent foraging and feeding (Sheffield and Thomas 1997). Nests are habitually found in burrows made by other animals or under rocks (Sheffield and Thomas 1997; Reid 2009). This animal is solitary, but a male and a female may remain together during the non-breeding season (Sheffield and Thomas 1997). The Virginia opossum is a small, highly opportunistic animal. It can live in many types of forested and open habitats and is generally found in the wetter areas of its range, near streams and swamps. It is known to frequently forage in human refuse piles and, as a result, is commonly found near human settlements (McManus 1974; Emmons 1997; Reid 2009). The diet of this omnivorous animal consists of insects and other invertebrates, small vertebrates, carrion, fruit, and other plant matter (Emmons 1997). Mainly active at night, the Virginia opossum spends most of its time travelling and feeding on the ground although it may climb readily (Emmons 1997; Reid 2009). It is known to “play dead” when disturbed or threatened (Emmons 1997; Reid 2009). The common opossum is similar in its habits to the Virginia opossum. It mainly lives on the ground, but may climb in trees to feed or escape danger (Emmons 1997; Reid 2009). This animal focuses on the exploitation of small animals (e.g., insects, worms, and small vertebrates), although regularly forages for fruit and other plant matter (Emmons 72 1997; Reid 2009). In addition, it frequently takes advantage of the presence of garbage dumps in rural areas (Reid 2009). At night, it may travel one to three kilometers in search for food, but it remains in well-defined home ranges (Reid 2009). This animal thrives in secondary forests and disturbed areas, although it is also found in mature, humid forests (Emmons 1997; Reid 2009). All felines found in the Maya subarea occupy the rainforests. Solitary hunters, they handle almost anything they encounter, including mammals, snakes, birds, turtles, caimans, fish, and even large insects (Emmons 1997). All species are believed to breed year-round in the tropics, with litter size varying from one to four kittens (Tewes and Schmidly 1987; Emmons 1997; Reid 2009). All species are mainly active nocturnally (Tewes and Schmidly 1987; Emmons 1997). The ocelot is a small feline that targets a variety of small- and medium-sized prey (e.g., rodents, birds, snakes, lizards, and other small vertebrates). It spends most of its time foraging on the ground and seldom climbs in trees (Tewes and Schmidly 1987; Emmons 1997; Reid 2009). The ocelot may occupy many different habitats (e.g., rainforest, tropical deciduous forest, secondary forest, and scrubs), as long as they provide sufficient cover (Tewes and Schmidly 1987; Emmons 1997; Reid 2009). It may also live in disturbed areas and near human settlements (Emmons 1997; Reid 2009). Slightly larger than a house cat, the margay is another small feline inhabiting tropical rainforests (Tewes and Schmidly 1987; Emmons 1997). This species is the most arboreal cat in the Americas. It hunts and rests in trees, but travelling is done on the ground (Emmons 1997; Reid 2009). As a consequence of its arboreal habits, the margay is found almost exclusively in mature and secondary forests and does not adapt well to human disturbance (Tewes and Schmidly 1987; Emmons 1997; Reid 2009). Small 73 mammals, birds, and reptiles form the bulk of its diet (Emmons 1997; Reid 2009). Strictly nocturnal, the margay spends daylight hours hidden among dense trees (Tewes and Schmidly 1987). Two large cats inhabit the tropical forests of the Maya subarea. The puma is a solitary animal, usually wary of humans (Emmons 1997; Reid 2009). This animal is highly adaptable and can be found in a variety of habitats, such as rainforests, scrubs, and mountains (Emmons 1997; Reid 2009). The jaguar is the largest cat in the Americas. It favors undisturbed forested habitats and waterside areas (Tewes and Schmidly 1987; Emmons 1997; Reid 2009). Both species predominantly prey upon medium- and largesized mammals, such as deer, peccary, agouti, and paca. Depending on local availability, they may also feed on turtles, caimans, birds, fish, and smaller mammals (Tewes and Schmidly 1987; Emmons 1997; Reid 2009). Jaguars and pumas are sedentary animals that presumably occupy defined home ranges (Tewes and Schmidly 1987; Emmons 1997). Both the black and green iguanas live in tropical moist and dry forests, although the black variety may also be found in open savannas (Campbell 1998). The green iguana is arboreal. It spends most of its time in trees and is normally found near permanent sources of water (e.g., rivers, streams, and lakes). In contrast, the black iguana lives closer to the ground and rests in underground burrows or hollow logs (Campbell 1998). Both species are primarily herbivorous, feeding on leaves, flowers, and fruit. It is reported that the black iguana can eat small birds, rodents, and reptiles. Females lay eggs during the dry season, from February to June (Campbell 1998). Mud and musk turtles (Kinosternidae) are found in shallow backwaters of streams and lakes, marshes, swamps, and aguadas. Generally, these turtles are only active 74 seasonally, because they bury themselves into the mud during the dry season (Campbell 1998). The northern giant musk turtle (Staurotypus triporcatus) is the only species living near large, permanent bodies of water and active year-round. These turtles are usually active at night. They are poor swimmers and forage at the bottom of ponds and lakes. They do not need to emerge from the water to bask (Campbell 1998). Their diet is composed of a mix of aquatic invertebrates, such as insects, shrimps, molluscs and crabs, vegetable matter, tadpoles, and carrion (Campbell 1998). These observations about the ecology and behavior of the most prevalent species recovered at Pacbitun are central to an interpretation of the subsistence behaviors of the Middle Preclassic Maya. However, before any interpretation can take place, the quantitative and taphonomic methods used in the analysis of the faunal remains need to be examined. They are the focus of the following chapter. 75 CHAPTER 5: METHODOLOGY In order to interpret subsistence strategies at Pacbitun, it is necessary to evaluate the integrity of the study sample. Indeed, multiple pre- and post-depositional processes may have altered faunal assemblages before and after their recovery by the archaeologist. Consequently, this chapter presents the methods used to assess taphonomic signatures on the Pacbitun assemblages, along with a description of the quantification methods used in the analysis of taxonomic composition and skeletal part representation. The chapter also considers why the chosen methods are appropriate for studying faunal assemblages recovered in tropical environments. 5.1 Definitions and identification procedures Several important concepts used throughout this analysis must be defined prior to any discussion regarding the faunal assemblages investigated in this study. A “skeletal element” refers to a single complete anatomical unit, such as a humerus or a molar. A “specimen” is described as any skeletal remain anatomically complete or a fragment thereof, such as a proximal humerus or a molar fragment. The implication is that all skeletal elements are specimens, but not all specimens are skeletal elements (Grayson 1984:16; Lyman 2008:5). The identification of faunal remains was carried using comparative collections from the Archaeozoology Laboratory at Trent University and the Department of Vertebrate Paleontology at the Royal Ontario Museum. Manuals by Olsen (1982), Barone (1986), and Gilbert (1993) were also consulted. Vertebrate remains were identified to the highest taxonomic level possible. All identified specimens were examined using a 10X magnification lens to observe surface modifications. 76 5.2 Quantification methods The Number of Identified Specimens (NISP) is a fundamental measure of faunal quantification (Grayson 1984; Lyman 2008; Reitz and Wing 2008). It is defined as the number of skeletal elements and fragments identified to taxon. Specimens counted in NISP are generally identified to the skeletal element and to at least the genus level (Lyman 2008:27). However, in this study, NISP values also include bird, reptile, and fish specimens identified to the class level, as these taxa could not always be identified as precisely as mammalian specimens. Isolated teeth were counted as separate elements if they could not be associated with another cranial element. If they were still in articulation with the maxilla or mandible, they were considered part of the cranial element and were not added to the NISP. When mammal bones could not be identified to family or genus, they were attributed to broader taxonomic groups (Table 5.1), following the body size classes defined by Savage (1971) and Emery (2007a). Table 5.1 Taxonomic groups based on body size. Small mammal Gopher Mouse Squirrel Medium mammal Domestic dog Armadillo Opossum Agouti Paca Small felines Rabbits Raccoons Large mammal White-tailed deer Brocket deer Tapir Jaguar Puma Peccary The Minimum Number of Elements (MNE) corresponds to the minimum number of skeletal portions necessary to account for all the specimens representing a particular element (Bunn and Kroll 1986:434–435; Lyman 1994:102). MNE estimates were determined by manually counting, for each skeletal element, the number of portions with 77 overlapping landmarks (Todd and Rapson 1988) or zones (Morlan 1994) for proximal and distal ends, as well as for shafts. Derived from MNE, the Minimum Number of Individuals (MNI) is a measure of abundance consisting of the smallest number of individuals necessary to account for all of the specimens of a particular taxon in an assemblage (Klein and Cruz-Uribe 1984; Lyman 2008). MNI values were calculated on the basis of the most common anatomical element for each taxon. For both MNE and MNI, age, sex, and specimen size were not taken into account, because the use of these characteristics tends to inflate the representation of diagnostic specimens, such as teeth and epiphyses, in comparison to less diagnostic specimens, for instance, long bone shaft and rib fragments (Morin 2012:68). Only stratigraphic provenience (early Middle Preclassic versus late Middle Preclassic deposits) was considered in the calculation of MNE and MNI estimates. MNE was used to measure both the frequencies of skeletal parts and the abundance of distinct individuals. Derived from MNE as well, the Minimal Animal Units (MAU) is used to describe skeletal part frequencies (Lyman 2008). MAU values were determined by dividing MNE estimates for each element by the number of times this element is represented in a complete skeleton. The values were then standardized (%MAU) by dividing all MAU values by the greatest MAU value in the assemblage (Binford 1984:50). This procedure reduces much of the variation in MNE values caused by the differential frequency of skeletal elements in a complete skeleton (Lyman 2008:233–237). A similar protocol was adopted for the use of NISP in the analysis of skeletal part frequencies. NISP counts for each skeletal element were divided by the number of times this element occurs in a particular taxon, resulting in a Normed NISP (NNISP) (Grayson and Frey 2004; Grayson and Delpech 2008). For example, NNISP values for long bones 78 were obtained by dividing the NISP counts by two. The same procedure was applied to cranial elements, as crania and mandibles are represented in the assemblages by isolated left and right fragments. NNISP counts were also standardized (%NNISP) to the abundance of the most common element for each taxon. 5.2.1 Strengths and weaknesses of NISP, MNE, and MNI The main advantage of NISP lies in its simplicity. NISP is a direct tally of identified specimens. As new specimens are identified and added to the analysis, the researcher does not have to recalculate the totals. NISP is also easily replicable. Two different observers, assuming comparable skills in identification and access to the same collections, should obtain similar NISPs for the same faunal assemblage (Grayson 1984:20; Klein and Cruz-Uribe 1984:25; Lyman 2008:28). In addition, because it is cumulative, NISP does not suffer from problems of aggregation between units or layers (Grayson 1984). One specimen is always considered to be one specimen no matter where it was found or how it is aggregated. Finally, as different analysts would likely tally NISP more or less the same way, NISP has the advantage of facilitating comparisons of assemblages from different sites. This is particularly true for Maya archaeozoology given that the majority of lowland Maya faunal analyses are based on NISP counts (Emery 1997:90). NISP does, however, suffer from various shortcomings. First, NISP is sensitive to inter-taxonomic and intra-taxonomic variation. Indeed, different taxa do not share the same number of skeletal elements and some taxa or elements may be more easily identified than others. Some skeletal elements or taxa are also more likely to be fragmented or destroyed as a result of differential structural density (Grayson 1984:20– 79 25; Klein and Cruz-Uribe 1984:25; Marshall and Pilgram 1993; Ringrose 1993; Lyman 2008:29–34). Given these problems, the abundance of certain elements or taxa may be under- or over-represented relative to their initial abundance in the deposited assemblage as assessed by NISP. Differential identification and fragmentation can be mitigated by refitting (discussed in section 4.3). Refitting is defined as piecing back together specimens that belong to the same skeletal element (mechanical refit) or by reassembling together skeletal elements from a same individual (anatomical refit) (Enloe and David 1989, 1992; Hofman 1992). Differential representation caused by differences in total number of elements between species can be controlled for with the use of additional quantification methods, such as normed NISP (NNISP). NISP is also plagued by the problem of interdependence (Grayson 1984; Lyman 2008; Reitz and Wing 2008:203), given that it does not account for the fact that multiple specimens identified to a taxon may be from a single individual. For instance, if the NISP is 50, it is not possible to determine whether those specimens represent 1 or 50 individuals. In this context, NISP may exaggerate the sample size of individuals or elements. The problem of interdependence may preclude the use of basic statistical tests as most require independent observations (Grayson 1984:23–26; Lyman 2008:36–38). A high degree of fragmentation may also amplify the problem of interdependence (Klein and Cruz-Uribe 1984:25; Marshall and Pilgram 1993). This drawback of NISP can partially be countered by conducting refit studies and by using derived quantification measures, such as the minimum number of individuals (MNI). MNI solves the problem of interdependence as it avoids counting the same individual twice. Similarly, it is not affected by the problem of inter-taxonomic variation of skeletal elements, as it is based on the most common skeletal element of a taxon in an assemblage (Lyman 2008:38–39, 44). 80 Although MNI was introduced to overcome the problems associated with NISP counts, several problems with this quantification method have also been identified. MNI is more difficult to tally than NISP as it is not cumulative. Moreover, there is no consensus on how MNI estimates should be derived (Klein and Cruz-Uribe 1984:26; Marean et al. 2001; Lyman 2008:46), which may reduce comparability between assemblages. This problem can, to some extent, be controlled for if the same methods are used (Klein and Cruz-Uribe 1984:26–28; Marean et al. 2001; Lyman 2008:46–48). Additionally, MNI counts can exaggerate the importance of rare taxa. This problem can be assessed if MNI estimates are considered together with NISP values (Klein and CruzUribe 1984:32–33; Plug and Plug 1990; Lyman 2008:46–47). MNI values can also be affected by sample aggregation. The MNI count for an entire site will likely differ from the MNI estimates calculated for multiple distinct units of the same site, because a given skeletal part might not constitute the most abundant element across different aggregates. For instance, although the left humerus of a given taxon might be the most abundant skeletal part at a site, other elements might occur more frequently if the assemblage is divided in multiple aggregates (Grayson 1984:29–30; Plug and Plug 1990; Lyman 2008:58–63). Refitting can help overcome the problem of aggregation, as it reduces the possibility of aggregates sharing specimens from the same individuals (Lyman 2008:68–69). The nonlinear increase of MNI with increasing sample size also constitutes a problem. Similar to NISP, MNI increases with fragmentation. However, as the intensity of fragmentation increases, it becomes increasingly difficult to identify fragments because they retain fewer and fewer diagnostic landmarks (Lyman and O'Brien 1987; Marshall and Pilgram 1993; Lyman 2008:43). At some point, the rate of increase of MNI will 81 decrease relative to the rate of increase of NISP (Marshall and Pilgram 1993) because the probability of adding a specimen of a new, unrepresented individual to MNI counts decreases concomitantly (Grayson 1984:61–64; Lyman 2008:48–50). Another derived measure, MNE, has many of the same advantages and problems. Like MNI, MNE is used to control for the problem of interdependence. MNE ensures that each element will not be tallied twice which helps to circumvent the problem of differential fragmentation. At first glance, MNE may represent a better unit than NISP for quantifying the abundance of skeletal parts (Lyman 2008:222). However, like MNI, MNE is influenced by strategies of aggregation and sample size (Lyman 2008:222–224). Due to the problems of differential preservation, fragmentation, and identification, NISP and MNI values cannot be considered as ratio-scale data (Grayson 1984:94–96). Nonetheless, NISP and MNI can provide reliable ordinal data when taxa are well separated in terms of abundance. Indeed, the greater the difference in abundance between taxa, the less likely that specimen interdependence (for NISP) or the use of different aggregation methods (for MNI) will alter the rank order of those taxa (Grayson 1984:97– 99; Lyman 2008:73–75). The same reasoning applies to MNE estimates (Lyman 2008:226–228). 5.2.2 Use of quantification methods in this study The small size of the Pacbitun assemblages may affect and limit the use of certain quantification methods. MNE derived counts, such as the MNI and MAU, are not, in comparison to NISP, particularly accurate when used to describe small samples (Grayson 1978; Plug and Plug 1990). This problem is also amplified by the high species diversity that characterizes the assemblages. As a result of small sample size, the results obtained 82 from statistical tests based on MNE and MAU values may not be very robust. To limit the problems associated with each quantification unit, NISP and MNE were used conjointly to measure taxonomic composition, whereas NNISP and MAU values were used to investigate skeletal part representation. The use of several quantification methods should increase the robustness of the results with respect to taxonomic composition and skeletal part representation. 5.3 Refitting Refitting is useful because conjoining two or more fragments together can increase the identifiability of otherwise nondiagnostic fragments, particularly long bone shaft fragments (Marean and Kim 1998). Additionally, the stratigraphic integrity of an archaeological sequence can be tested through an analysis of the provenience of the refitted fragments (Hofman 1992; Morin et al. 2005). Although refitting an entire faunal assemblage is tedious and time-consuming (Marean and Kim 1998), even partial refitting of an assemblage can provide substantial information on occupation mixing (Morin et al. 2005). Because of the small sample size of the Pacbitun assemblage, it was possible to attempt to refit all long bone shaft fragments, rib fragments, and taxonomically identified specimens. Efforts were made to refit unidentified shaft fragments with other specimens from the same unit. Identified specimens were tentatively refitted with other fragments from the same unit, as well as with all specimens belonging to the same element and taxon. This procedure was carried out across all levels. A distinction was made between dry bone and green bone given that they can yield information on site formation processes and occupation mixing (Todd and Stanford 1992). 83 5.4 Age and sex The analysis of animal age and sex can produce important information on seasonality of occupation, human prey choice, and husbandry practices. Epiphyseal fusion is a common method used to estimate the age at death of particular individuals in faunal assemblages. Because bones often fused successively during the life of animals, the sequence of fusion can be used to establish coarse age classes, particularly for juvenile specimens (Reitz and Wing 2008:72). However, when all the bones of a skeleton are fused, it is seldom possible to distinguish between stages of older individuals (e.g., prime adults versus senile individuals). Therefore, epiphyseal age classes may only provide coarse information on mortality profiles. This problem may be accentuated by the fact that unfused epiphyses are more easily affected by destructive processes (e.g., carnivore gnawing, post-depositional processes) than fused ones, which can lead to biases against younger individuals (Klein and Cruz-Uribe 1984:41–43). Fortunately, the use of teeth for estimating age frequently yields more precise information than epiphyseal fusion. First, teeth are generally more durable than epiphyses and are less likely to be damaged by post-depositional destruction (Klein and Cruz-Uribe 1984:43–44). Second, teeth erupt at a certain age and wear down more or less continuously throughout the life of an animal (Klein and Cruz-Uribe 1984:43–44; Reitz and Wing 2008:72–73). Consequently, the relative age of mammals can often be estimated by using extant sequences of dental eruption and wear (Klein and Cruz-Uribe 1984:46–55; Hillson 2005:215–222). Age for worn teeth is frequently measured with the maximum height of the crown of cheek teeth, both deciduous and permanent (Payne 1973; Hillson 2005:214–222; Reitz and Wing 2008:72–73). However, the method 84 requires complete teeth, which can limit the number of specimens suitable for constructing age profiles (Klein and Cruz-Uribe 1984:52–54). Additionally, there can be significant variation in dental eruption and wear between populations (Klein and CruzUribe 1984:52) and, in some species, between sexes (Gee et al. 2002; Hillson 2005:223). Data is not always available for wild animals (Klein and Cruz-Uribe 1984:41–43), but both biologists (e.g., Severinghaus 1949; Gilbert and Slolt 1970; Gee et al. 2002) and archaeologists (e.g., Elder 1965; Wolverton et al. 2008) have been successful in using this method for white-tailed deer, the most common species at Pacbitun. At Pacbitun, age determination focused on white-tailed deer. Data on epiphyseal fusion was compared to sequences recorded by Purdue (1983). Epiphyses were coded as unfused, intermediate, or fused. Bones in the intermediate category are those for which the line of fusion is still clearly visible. Age from teeth was estimated using measurements provided by Severinghaus (1949). Crown height measurements were recorded for mandibular premolars and molars. Following the approach adopted by Gee and colleagues (2002), specimens were assigned to one of three age categories: juvenile (<1 year old), subadult (1–2 years old), and adult (>2 years old). The adult class was subsequently split into young and old adults based on dental wear. When possible, age was also determined for other species if published sequences of epiphyseal fusion or dental eruption and wear were available. Concerning sex determination, one of the simplest methods consists of recording the presence or absence of antlers for ungulates (Klein and Cruz-Uribe 1984:39–40). Sex can also be determined based on osteometric differences between males and females. However, this technique requires bone specimens sufficiently complete to allow adequate 85 measurements to be taken (Klein and Cruz-Uribe 1984:39–41). The absence of antlers, small sample size, and substantial fragmentation prevented sex determination at Pacbitun. 5.5 Taphonomic modifications Anthropic, biological, chemical, and physical factors may all affect archaeological assemblages and distort the interpretation of human behaviours inferred from faunal analyses. Therefore, multiple lines of evidence are examined here in order to determine which agent(s) is(are) responsible for the formation of the faunal assemblages at Pacbitun. 5.5.1 Fractures Although taphonomic and actualistic studies have shown that there is no simple correlation between a type of fracture and the agent that produced it (Binford 1981; Haynes 1983b; Johnson 1985), the study of fracture morphology can help to infer the timing of bone fracturing. The importance of studying fracture morphologies on long bone fragments should be emphasized because fractures constitute constant properties of broken bones (Villa and Mahieu 1991). It may be possible to study fractures even when cortical surfaces are heavily weathered, as is frequent in tropical environments, or when cutmarks or gnawing marks have become obscured by poor surface preservation. In this study, fractures on long bone fragments have been assigned to two types: green-bone and dry-bone fractures. Green-bone fractures tend to have a homogeneous color and show a smooth texture and spiral shape (Morlan 1980:48–49; Haynes 1983a; Johnson 1985:176, 222). Dry-bone fractures often exhibit a rough texture in cross-section, have a more or less transverse shape and may present a different color than the outer cortical surface (Morlan 1980:48–49; Johnson 1985:176–178, 222). Only unambiguous 86 fractures were recorded following this procedure. Although this method has mainly been used with mammal remains, it can also be applied to the analysis of avian long bones (Higgins 1999; Serjeantson 2009). Additionally, following the terminology of Villa and Mahieu (1991), the shape of proximal and distal fractures on long bones was assigned to one of the following types: curved, v-shaped, oblique, transverse, irregular, or ragged. Fracture edges were recorded following Villa and colleagues (2005) as fresh, slightly abraded, abraded, and very abraded, as this information can potentially help to infer about site formation processes. 5.5.2 Butchery and tool use Butchery can be defined as all sets of human activities, such as skinning, disarticulation, and meat removal, associated with the extraction of consumable resources from an animal carcass (Lyman 1994:294–296). Cutmarks can result from such actions (Binford 1981:46–47; Bunn 1983b), as well as from the manufacture of bone tools (Emery 2008a). Therefore, cutmarks constitute the best indicator of human involvement in assemblage formation (Villa et al. 2004). Because they can be mistaken with marks produced by the action of carnivores or by trampling, only unambiguous cutmarks were recorded in this analysis. Marrow constitutes an important source of fat and nutrients. Bones are generally cracked open by humans with a hammerstone-on-anvil technique, which may leave percussion marks and notches (Johnson 1985:192–194; Pickering and Egeland 2006). Because they penetrate the thickness of the bone, notches are less easily obscured by weathering than marks left on the cortical surface of the bone. As a result, they can be used, with some limitations, to identify the agents responsible for the formation of 87 archaeological assemblages (Capaldo and Blumenschine 1994). Unfortunately, notches made by carnivores can be very similar to notches produced by humans (Bunn 1989). Nonetheless, Capaldo and Blumenschine (1994) suggest that the morphology of notches produced by humans and carnivores can be statistically distinguished for small bovids (less than 115 kg). In a recent study, Galán and colleagues (2009) observed considerable overlap between carnivore-induced and hammerstone-induced notches on small bovid assemblages and concluded that the pattern for small bovids is much weaker than proposed by Capaldo and Blumenschine. Castel (2004) also noticed that, in some instances, the morphology of notches produced by wolves on sheep bones can be similar to that produced by human activities. Despite this lack of agreement in the literature, all notches were recorded in this study. Because of the marginal presence of carnivores in the Pacbitun assemblages (see Chapter 6), it is believed that notches are probably the result of anthropogenic fracturing. The Maya manufactured a wide range of artifacts (e.g., needles, scrapers, fishhooks, beads, pins, and musical instruments) from bone, tooth, and antler (Hamblin 1984; Pohl 1990; Moholy-Nagy 1994:110; Emery 2008a, 2009). Bone artifacts recovered from Maya sites, such as Tikal (Moholy-Nagy 1994) and Dos Pilas (Emery 2008a, 2009), indicate that these were generally made of mammalian bones. The Maya preferentially selected the straightest and strongest bones for this purpose, in particular the tibia, femur, and metapodial (Hamblin 1984; Emery 2008a, 2009). Bones from white-tailed deer was the preferred raw material, but other medium and large mammals (felids, peccary, dog, and brocket deer) were also exploited (Moholy-Nagy 1994:107; Emery 2008a, 2009). Fragile cranial fragments and scapulae might also have been selected for the production of disks and other flat artifacts (Moholy-Nagy 1994:107; Emery 2008a, 2009). In some 88 cases, the edges of broken bones were used as tools without further shaping. These expedient tools can be identified by the polish visible on the bone surface (Pohl 1990:158). One artefact made from a mammal long bone was identified in the sample. Bone debris resulting from artifact production may also be present, but were not identified during the analysis. 5.5.3 Carnivore ravaging Carnivores can be important agents of accumulation and transformation of faunal assemblages. Unfortunately, studies focusing on the action of carnivores in tropical environments are rare. The literature, however, abounds with actualistic and archaeological studies in other areas of the world (e.g., Binford 1981; Marean and Spencer 1991; Stiner 1994). These provide considerable insight on how to recognize the signature of carnivore agents in faunal assemblages. The most destructive agent at Maya sites is likely to have been the domestic dog (Stanchly 2004). As companions, dogs possibly scavenged household waste or were fed butchery scraps (Pohl 1990; van der Merwe et al. 2000; Stanchly 2004). Therefore, they could have both accumulated and transformed the faunal assemblages at Pacbitun. Dogs can cause extensive damage to animal bones. They often destroy the cancellous epiphyses, gnawing the ends into the shaft to extract fat. Relatively complete shafts or “bone cylinders” may remain from this process (Binford 1981; Johnson 1985:191–192; Cruz-Uribe 1991; Castel 2004). In contrast, humans tend to break bones along the midshaft, which results in a high proportion of fragmented bones or “splinters” (Bunn 1983a; Pickering and Egeland 2006). Therefore, long bone shaft fragmentation (see section 4.5.4) is an important aspect to consider when determining the impact of carnivores on a 89 faunal assemblage. It should be noted that dogs can also fracture bones through static loading, producing notches and pits (Johnson 1985:192; Capaldo and Blumenschine 1994; Castel 2004). In dog experiments, punctures and furrows occur frequently on the epiphyses, while scoring and pitting are more common on the diaphysis (Binford 1981:44–49). Dogs also tend to swallow bone fragments or small bones while eating. These bones may be chemically eroded to varying degrees during digestion (Andrews and Evans 1983). Pumas and jaguars also accumulate and modify faunal assemblages, but not as actively as other carnivores (Seymour 1989; Martín and Borrero 1997). Large cats rarely cause heavy gnawing damage, because they do not tend to consume grease and marrow contained in bones. However, they can leave few, relatively deep and large punctures and furrows on the epiphyses (Haynes 1983b; Martín and Borrero 1997; Montalvo et al. 2007; Mondini and Muñoz 2008; Muñoz et al. 2008). Smaller felids, including the ocelot, margay, and jaguarundi, may also significantly damage small mammal (<5 kg) bones (Álvarez et al. 2012), but are less likely to cause important damage to large carcasses. Although felids do not tend to come near human settlements and rarely scavenge on carcasses (Seymour 1989), they nonetheless could have accumulated or modified the faunal assemblages at Pacbitun. Other animals present in the habitats surrounding Pacbitun can potentially accumulate or alter faunal assemblages. Procyonids (e.g., coati, raccoon, and kinkajou) are omnivorous. They feed mainly on fruits and invertebrates, and occasionally on small rodents and birds (Lotze and Anderson 1979; Ford and Hoffmann 1988; Gompper 1995, 1996). Mustelids, including the long-tailed weasel and tayra (Eira barbara), are carnivorous. They consume a variety of insects and small vertebrates, including small 90 rodents, rabbits, iguanas, and birds of small to medium size (Sheffield and Thomas 1997; Presley 2000). Therefore, despite their small size, mustelids and procyonids may prey on the same small taxa as humans do. Some species may live near human habitations, taking advantage of food found in gardens, orchards, and agricultural fields (Ford and Hoffmann 1988; Gompper 1995, 1996; Presley 2000). These carnivores probably have little impact on the bones of large animals, because their carnassial teeth are poorly developed compared to larger carnivores (Ford and Hoffmann 1988; Gompper 1995). However, they are known to accumulate small-sized vertebrates, particularly in dens and burrows (Andrews and Evans 1983). Lastly, rodents, such as the agouti and paca, also transport and gnaw bones. Rodent gnaw marks can easily be identified because of the distinctive furrows they produce with their incisors (Binford 1981; Johnson 1985:180). Following Binford (1981:44–51), carnivore gnaw marks were classified in this study as tooth pits, punctures, crenulated edges, scoring, furrows, scooping, and traces of digestion. The extent of carnivore gnawing was also recorded as marginal, limited to one section, or extensive (Morin 2012:73). Because both surface preservation and bone fragmentation can affect the observation of marks on bones, data on fragment size, completeness and circumference of long bone shafts is also required to understand animal activity. 5.5.4 Fragmentation The study of bone fragmentation can reveal the extent of anthropic and animal action at a site, as well as convey information on the impact of taphonomic disturbance. As mentioned earlier, human activities generally tend to produce a majority of splinters, whereas assemblages deposited by carnivores are frequently characterized by a high 91 proportion of long-bone cylinders with deleted epiphyses (Binford 1981:171–177; Bunn 1983a, 1989; Villa et al. 2004). Several measures of fragmentation were used in this analysis. First, maximum length and maximum width were measured for all identified specimens. Length of all unidentified specimens was also recorded using 1 cm size classes. The circumference of long bone fragments was described as follows: less than half of the original circumference (<1/2), more than half (>1/2), or complete (Bunn 1983a; Villa and Mahieu 1991). Similarly, all long bone shafts were coded as a fraction of the original length: less than one quarter (<1/4), between one quarter and one half (1/4–1/2), less than three quarters (1/2–3/4), and three quarters to complete (>3/4) (Villa and Mahieu 1991). Finally, long bone fragments were recorded using a simple system of five bone portions: proximal end, proximal shaft, middle shaft, distal shaft, and distal end (Marean and Spencer 1991). 5.5.5 Burning Burned bones are generally considered direct evidence of anthropogenic activity (Stiner et al. 1995; Villa et al. 2004). Intentional burning of bones can result from cooking, disposal of rubbish in fires, use of bones as fuel, or cremation (Gilchrist and Mytum 1986; Nicholson 1993; Villa et al. 2004). Bones can also be burned accidentally in a natural fire or due to their proximity to a fireplace (Gilchrist and Mytum 1986; Villa et al. 2004). Burned bones can exhibit different colors, these being a function of the maximum temperature reached by the bone (Nicholson 1993; Lyman 1994:385; Stiner et al. 1995). Bones that are slightly burned tend to be brownish. When reaching carbonization, they 92 turn black. As the intensity of the fire increases to calcination, bones shift from black to gray to white, sometimes passing through shades of blue or green (Shipman et al. 1984; Gilchrist and Mytum 1986; Nicholson 1993; Stiner et al. 1995). Burned bones tend to be more brittle than unburned bones. Their mechanical strength varies according to the extent to which they have been burned. Indeed, as burning intensity increases, bone become more friable and porous (Gilchrist and Mytum 1986; Stiner et al. 1995). Consequently, fragment size can be an important variable in determining burning intensity (Stiner et al. 1995). As bones become more susceptible to fragmentation, they may lose some of their diagnostic features, hindering taxonomic and skeletal identification. Bones will not necessarily be destroyed by burning, but rather may become analytically absent as they slowly become unidentifiable (Lyman and O'Brien 1987; Buikstra and Swegle 1989; Lyman 1994:391; Stiner et al. 1995). In this study, the color of burned bones (brown, black, gray, green, blue, or white) was recorded for the entire assemblage. This method was chosen because colors are easily discernible to the naked eye and have proven reliable for diagnosing burning damage on archaeological bones (Stiner et al. 1995). The maximal length in centimeters of all burned fragments was also recorded to document fragmentation of the burned portion of the assemblage. 5.5.6 Additional taphonomic agents Post-depositional processes may have an impact on the preservation of faunal assemblages and affect the identification of marks left on bones. Several types of alterations were recorded for all specimens: exfoliation, sheeting, root etching, staining, and cracking. Exfoliation can be defined as the loss of the first few millimeters of cortical 93 bone, while sheeting describes the fracturing of cortical bone into one or more sheets that tend to be parallel to the cortical surface (Morin 2012:70). The six weathering stages identified by Behrensmeyer (1978) were not used in this study, because the criteria of cracking, flaking, and splintering used to categorize bone preservation were seldom observed on the Pacbitun assemblages. This is probably explained by the significant differences existing between the Belizean tropical rainforest and the Kenyan savannah where Behrensmeyer’s experiments were conducted. In a different study, Tappen (1994) suggested that bone modifications caused by weathering in a savannah climate differ from those in a tropical rainforest. She observed that subaerial weathering, which caused the most important damage to the bones studied by Behrensmeyer, was slower in rainforests. She attributed this to the reduced sunlight, high moisture, and low variation of humidity and temperature distinctive of tropical rainforests. She occasionally observed exfoliation on the cortical surface of the bones, which is generally attributed to the chemical action of natural acidic soils and biological agents, such as roots, algae, and fungi (Tappen 1994; Fernández-Jalvo et al. 2002). This observation applies particularly to the Pacbitun assemblages, as it is the most common damage observed on the faunal remains. As Tappen does not provide a methodology to study specifically bones recovered in tropical environments, bone surface condition was observed and assigned to one of four categories: intact, slightly damaged, damaged, or poor (Morin 2012:71). In this classification, a surface is considered intact when almost no surface damage is recorded. A surface with superficial damage is considered slightly damaged. This would be the case for a bone surface with local damage, but with visible marks or morphological features. When landmarks are faint and the surface is significantly altered, the specimen is coded 94 as damaged. Poorly preserved bones have a considerably damaged cortical surface. Marks on this type of surface are unlikely to have survived. Finally, an estimate of the percentage of the remaining original bone surface was also recorded by 10% intervals (E. Morin, personal communication, 2012). 5.6 Summary The methods described in this chapter, which are used in the analysis of the Pacbitun assemblages, will provide detailed taphonomic and quantitative data about the foraging strategies adopted by the Preclassic Maya at Pacbitun. The next chapter examines the stratigraphic and taphonomic integrity of the study sample. 95 CHAPTER 6: SAMPLE DESCRIPTION AND TAPHONOMY This chapter assesses the integrity of the Pacbitun faunal assemblages. It begins with a description of the material analyzed in this study, while the second half focuses on measuring the impact of different taphonomic processes on the Middle Preclassic samples. 6.1 The Pacbitun faunal assemblages The faunal assemblages examined in this study date exclusively to the Middle Preclassic period (900–300 BC). The animal remains that were analyzed were recovered in Plazas A, B, C, and D during the excavations conducted from 1995 to 1997 by the Trent University-Preclassic Maya Project and from 2008 to 2011 by the Pacbitun Regional Archaeological Project (PRAP). The material recovered during the 1995 and 1996 field seasons has previously been identified by Norbert Stanchly. However, it was decided that this material would be reanalyzed in this study because different methods were used to assess the impact of taphonomic processes. The samples were retrieved from both primary (floor and perimeter deposits) and secondary contexts (fill and midden) (Table 6.1). The assemblages of vertebrate remains recovered from Pacbitun include a total of 1,730 specimens, with 566 specimens dating from the early Middle Preclassic and 1,164 from the late Middle Preclassic (Table 6.1). Most of the assemblages consist of unidentifiable mammal fragments (n = 1,110) and indeterminate specimens (n = 328). The use of refitting during analysis reduced the initial NISP count by 39.0%, for a postrefit total of 292 identified specimens (Table 6.2). Only post-refit NISP counts are used in 96 the following analysis because they help to mitigate problems of differential fragmentation and identification, as well as minimize the problem of specimen interdependence (Morin 2012:75). As such, post-refit NISP constitutes a more accurate estimate of taxonomic composition and skeletal part representation than pre-refit NISP. Table 6.1 Number of specimens by primary and secondary contexts for the Middle Preclassic assemblages. Contexts Primary contexts Floor deposits Perimeter deposits Secondary contexts Plaza fill Construction fill Secondary midden Total early Middle Preclassic n late Middle Preclassic n Total n 451 84 357 139 808 223 2 29 0 566 26 21 621 1164 28 50 621 1730 Table 6.2 Pre- and post-refit NISP counts by time period. Time period early Middle Preclassic late Middle Preclassic Total Total bone count 566 1164 1730 Pre-refit NISP* n 210 269 479 Post-refit NISP n 125 167 292 * Pre-refit counts include all refitted fragments. Mammals are the most frequently identified animals in the samples (96.8% of the total assemblages, Tables 6.3 and 6.4). Artiodactyls, including the white-tailed deer, peccary, and red brocket deer, dominate both the early Middle Preclassic (56.8%) and late Middle Preclassic samples (66.5%). Armadillos are the second most abundant taxon (12.0%). Carnivores, represented by the domestic dog, coati, weasel, and various felines (jaguar, puma, margay, and ocelot), represent 4.0% and 3.6% of the early Middle 97 Preclassic and late Middle Preclassic samples, respectively. Other identified mammals collectively form less than 8.0% of the assemblages and include the pocket gopher, opossum, tapir, paca, agouti, and rabbit. It should be noted that the collared peccary (Pecari tajacu) and white-lipped peccary (Tayassu pecari) are considered difficult to differentiate osteologically (Olsen 1982; Emery 2010:64). The limited comparative collections available to the author did not permit taxonomic distinction between the two species. Table 6.3 Distribution of faunal remains by zoological class for the early and late Middle Preclassic samples at Pacbitun. Taxon Mammals Reptiles Fish Birds Amphibians Total early Middle Preclassic n % 405 94.8 14 3.3 6 1.4 2 0.5 0 0.0 566 100.0 late Middle Preclassic n % 952 97.6 17 1.7 2 0.2 3 0.3 1 0.1 1164 99.9 Total n % 1357 96.8 31 2.2 8 0.6 5 0.4 1 0.1 1730 100.0 Reptiles form the second most important class (2.2%) in the assemblages. This group is dominated by turtle (early Middle Preclassic = 8.8%; late Middle Preclassic = 3.6%). Most turtle remains are carapace or plastron fragments lacking taxonomically diagnostic features. Only one specimen was specifically identified as a mud turtle. Snakes (3.1%) represent the second most common reptile group, with six colubrid and three viper remains. Remains of iguanas (1.7%) constitute the only specimens of lizards identified in the samples. 98 Table 6.4 Identified taxa by NISP and MNI for the early and late Middle Preclassic samples at Pacbitun. Scientific Name Osteichthyes Ictaluridae Serranidae Sparisoma spp. Unidentified fish Amphibia Rhinella marina Reptilia Iguanidae Testudines Kinosternon spp. Colubridae Viperidae Aves Galliformes Unidentified bird Mammalia Didelphis marsupialis Didelphis virginiana Common Name early Middle Preclassic NISP % MNI % late Middle Preclassic NISP % MNI % Catfish Grouper Parrotfish 1 1 4 0.8 0.8 3.3 1 1 - 4.2 4.2 - 1 1 0.6 0.6 1 - 4.2 - Marine toad - - - - 1 0.6 1 4.2 Iguana Turtle Mud turtle Colubrid Viper 2 11 1 - 1.6 8.8 0.8 - 1 1 1 - 4.2 4.2 4.2 - 3 5 1 5 3 1.8 3.0 0.6 3.0 1.8 1 1 1 1 4.2 4.2 4.2 4.2 Turkey, guan 2 1.6 1 4.2 1 2 0.6 1.2 1 - 4.2 - 2 1.6 1 4.2 1 1 0.6 0.6 1 1 4.2 4.2 17 13.6 4 16.7 18 10.8 2 8.3 1 1 1 1 1 2 6 1 0.8 0.8 0.8 0.8 0.8 1.6 4.8 0.8 1 1 1 1 - 4.2 4.2 4.2 4.2 - 2 1 1 1 1 1 1 7 6 1.2 0.6 0.6 0.6 0.6 0.6 4.2 3.6 1 1 1 1 1 - 4.2 4.2 4.2 4.2 4.2 4.2 - 51 40.8 2 8.3 88 52.7 3 14.8 7 4 1 3 2 2 125 5.6 3.2 0.8 2.4 1.6 1.6 100.1 1 2 1 1 1 24 4.2 8.3 4.2 4.2 4.2 100.0 10 3 1 2 167 6.0 1.2 0.6 1.2 100.0 1 1 1 1 24 4.2 4.2 4.2 4.2 100.0 Common opossum Virginia opossum Nine-banded Dasypus novemcinctus armadillo Canidae Dog, fox Canis lupus familiaris Domestic dog Nasua narica White-nosed coati Mustela frenata Long-tailed weasel Felidae Cats Puma concolor Cougar, puma Panthera onca Jaguar Leopardus wiedii Margay Leopardus pardalis Ocelot Tapirus bairdii Tapir Artiodactyla Artiodactyl Tayassuidae Peccary Cervidae Cervid Odocoileus White-tailed deer virginianus Mazama americana Red brocket deer Orthogeomys spp. Pocket gopher Dasyproctidae Agoutis, pacas Cuniculus paca Paca, gibnut Dasyprocta punctata Agouti Sylvilagus spp. Rabbit Total 99 Fish remains were rarely encountered during analysis (0.6% of the total assemblages). The only identified specimen of freshwater species is a catfish vertebra, whereas marine species are represented by remains of grouper and parrotfish. Identification of archaeological fish remains from Maya sites is generally considered challenging due to high species diversity, the non-diagnostic nature of many post-cranial fragments, and the propensity of fish remains to preserve poorly (Hamblin 1984; Powis et al. 1999; Stanchly 2004; Wake 2004a). Bird remains are also uncommon at the site (0.4% of the total assemblages). One specimen is identified as a gallinaceous bird. Although the high level of fragmentation precluded identification, the comparative material suggests the presence of medium- to large-sized birds. The amphibian assemblage is composed of a single bone from a marine toad. Overall, mammals dominate the Middle Preclassic assemblages, while reptiles, fish, and birds only form a fraction of the material. Before discussing the significance of these observations regarding taxonomic composition, the second half of this chapter considers taphonomic processes that possibly affected the Pacbitun faunal samples. 6.2 Taphonomy Taphonomy is a field of study that has received little attention from Maya archaeozoologists. In fact, published papers dealing specifically with the taphonomy of Maya faunal assemblages are nearly nonexistent (for an exception, see Stanchly 2004) and taphonomy is rarely addressed in the studies of animal resource exploitation. The impact of taphonomic processes in assemblage formation is examined in dissertations by Pohl (1976:67–81), Shaw (1991:243–249), and Emery (1997:72–92), but the scope of these analyses remains limited. 100 This bias may be attributed to the generally accepted idea that unfavorable tropical environments are mainly responsible for poor preservation of organic remains at Maya sites. Although high soil acidity and humidity likely constitute the main factors responsible for the rapid deterioration of organic remains in the tropics, many other natural and cultural processes may also have impacted the preservation of faunal remains. Therefore, as pointed out by Stanchly (2004), it is necessary to conduct detailed taphonomic analyses in order to identify the processes that might have shaped past faunal assemblages. The following section considers taphonomic factors relevant to the interpretation of the faunal samples at Pacbitun, including recovery methods, postdepositional attrition, burning, differential fragmentation and preservation, and carnivore ravaging. 6.2.1 Testing the stratigraphic sequence Bone refits were used in this analysis to test the stratigraphic integrity of the faunal assemblages. A total of 81 refit sets were found in the Middle Preclassic assemblages, for an average of 3.3 specimens per set. Seventy-two of these sets are refits on dry-bone fractures and likely represent post-depositional breakage. Several specimens were also refitted on recent breaks probably produced during or after the excavations. All dry-bone refits are intra-level sets from the same unit. No anatomical refit was identified. Because fractures on green bone are produced during the occupation of the site, they are more informative about site formation processes than dry-bone fractures (Morin et al. 2005). Nine sets of fragments involve green-bone fractures. Eight of them match specimens found within the same level of the same unit. Only one refit set on green-bone fracture is indicative of level disturbance, as it involves two fragments of a white-tailed 101 deer metacarpal recovered from an early Middle Preclassic deposit (Unit 2, Level 6b) and a late Middle Preclassic deposit (Unit 3, Level 4). Overall, all but one refit involve fragments found in close proximity to one another. This suggests that post-depositional disturbance was limited at Pacbitun. This interpretation seems congruent with what was observed during the excavations at Plaza B. Although the Maya had the habit of constructing new structures on top of older ones or modifying existing structures for new purposes (Garber et al. 2004a:25), the substructures at Plaza B do not seem to have been affected by this practice (T. G. Powis, personal communication, 2013). Indeed, the sub-structures appear to have been protected from later modifications by the thick midden that was laid over them at the end of the late Middle Preclassic period. The presence of intact floor and alleyway surfaces (i.e., primary deposits) for both the early and late Middle Preclassic structures provides additional evidence for limited post-depositional disturbance. Additionally, no re-use of stones from the Middle Preclassic platforms for later constructions was observed (T. G. Powis, personal communication, 2013). Concerning the late Middle Preclassic faunal remains recovered from the midden deposit, the small size of the artifact sample from this layer suggests a secondary nature (Hohmann and Powis 1999; T. G. Powis, personal communication, 2013). Nevertheless, the covering of the plaza with construction fill during the Late Preclassic and Late Classic (Hohmann and Powis 1996) seems to have protected the midden deposit from disturbance during later time periods. 102 6.2.2 Recovery methods The techniques used in the recovery of archaeological artifacts can affect sample composition in terms of species and skeletal representation, particularly when different screening methods are used (Payne 1975; Shaffer 1992; Emery 2004b). At Pacbitun, all deposits were dry-sieved in the field using a 1/4 inch (6.35 mm) mesh screen. However, excavation methods were not constant given that a 1/16 inch (1.2 mm) mesh screen was used to wet-sieve all floor deposits from Sub-Structures B-1 and B-2 in 2008 and 2009. This variation in mesh size may affect the analysis of the Pacbitun samples. Indeed, studies have shown that the exclusive use of large sieves (i.e., 1/4 inch) typically creates a bias towards the recovery of large specimens (Casteel 1972; Shaffer 1992; Wake 2004b), whereas the use of finer mesh sizes often improves the recovery of smaller specimens, including that of fish, birds, and rodents (Shaffer and Sanchez 1994; Masson 2004b; Wake 2004b; Serjeantson 2009). Therefore, it is necessary to consider the impact of the recovery methods on the abundance of small fragments at Pacbitun. The difference between the samples sieved with 1/4 (6 mm) and 1/16 (1.2 mm) inch mesh screen is not statistically significant (Kolmogorov-Smirnov D = 0.33, p = 0.81, Figure 6.1). This suggests that, although different recovery methods were used during the excavations, they did not influence the representation of small bone fragments. The size distribution of the fragments in Figure 6.1 also indicates that the Pacbitun assemblages are highly fragmented, with 74.2 % of the material classified as smaller than 2 cm, whereas less than 4.5% of the specimens are larger than 4 cm. The lowest size category (<1 cm) may be artificially depressed, because faunal specimens of this size are often not systematically collected. This partly results from the difficulty of sorting bones smaller 103 than 0.5 cm, particularly when large quantities of minute bone fragments are present in faunal assemblages (Villa et al. 2004). 60 1/4 inch (n = 1278) % of specimens 50 1/16 inch (n = 452) 40 30 20 10 0 <1 1–2 2–3 3–4 4–5 5+ Length in cm Figure 6.1 Fragment size distribution by screen size for all faunal specimens in the Pacbitun Middle Preclassic assemblages. Frequencies of identified species for both sieve sizes were also compared (Table 6.5). Intuitively, one would expect to recover a higher frequency of small animals when a smaller screen mesh is used. However, at Pacbitun, the use of a 1/16 inch mesh screen did not lead to the recovery of a higher frequency of small animals, such as fish, birds, or rodents (D = 0.22, p = 0.95). These results suggest that the use of a finer mesh size at Pacbitun did not result in an increased recovery of smaller fragments or taxa. However, other factors might have prevented the preservation of small specimens or species. These possibilities are explored in section 6.2.8 which provides a more detailed discussion of the taphonomy of fish and birds in the Pacbitun assemblages. In essence, it can be concluded that the use of two 104 different sampling strategies at Pacbitun has not greatly affected the assemblages in terms of fragment size and taxonomic composition. Table 6.5 Taxonomic representation in the Middle Preclassic samples by mesh size, in percentages. Taxon White-tailed deer Brocket deer Peccary Armadillo Agouti/paca Reptiles Small rodents Fish Birds Total 1/4 inch (6 mm) 48.4 6.9 5.9 15.4 1.6 13.3 3.2 3.7 1.6 100.0 1/16 inch (1.2 mm) 64.9 5.4 2.7 8.1 5.4 8.1 1.4 1.4 2.7 100.0 6.2.3 Density-mediated attrition In general, bones with low structural density are more prone to destruction by taphonomic processes than bones of higher mineral densities (Lyman 1994). This is because bone density is correlated with bone porosity. As the porosity of a given bone increases, so does the surface area per volume. As a result, mechanical and chemical attrition should affect more intensely bones of high porosity (or low density) simply because there is a greater surface to work on (Lyman 1982, 1994). This observation is particularly important for this study, as the effects of acidic soils, water leaching, and plant and tree roots commonly observed on Maya faunal assemblages may preferentially damage and destroy bones of low density (Stanchly 2004). In addition, because their pores are filled with grease (Brink 1997), the spongy low-density portions of bones are attractive to humans and carnivores. These parts can possibly be removed from faunal assemblages by carnivore ravaging and human 105 activities, such as grease extraction and the use of bone as fuel (Binford 1981; Lyman 1982, 1994; Brink 1997; Morin 2010). Bone parts of high structural density are more likely to be targeted for object manufacture, because dense sections of bones are often preferred for tool and ornament production (Lyman 1982, 1994; Stanchly 2004; Emery 2008a, 2009). In addition to anthropic and carnivore destruction, transport decisions may produce correlations with density, particularly when low-density elements (e.g., vertebrae) are discarded at kill sites (Binford 1978, 1981). For instance, vertebrae and crania were rarely encountered in the Pacbitun assemblages, but this might result from transport selectivity. Skulls may also have been preferentially used in the making of headdresses (Pohl 1981; Brown and Sheets 2000). To avoid this problem, only long bone portions were considered for examining density-mediated attrition in this study. Long bones are good candidates for this type of analysis because they are characterized by heterogeneous density, shafts usually being significantly denser than epiphyses. Additionally, long bones should not be affected by transport decisions to the same extent as low-density elements, given that it is unlikely that long bone shafts and epiphyses were transported separately (Binford 1981). To determine if density-mediated taphonomic processes have affected the Pacbitun assemblages, frequencies of long bone portions of white-tailed deer were compared to density values. Although density values are available for deer (Odocoileus spp.), the method used by Lyman (1982, 1994) does not exclude the volume of the internal cavity and, therefore, significantly underestimates true bone density (Lam et al. 1999; Lam et al. 2003). Consequently, values for reindeer (Rangifer tarandus) were used 106 instead (Lam et al. 1999) (Table 6.6). Data from the early and late Middle Preclassic periods were considered together because of small sample size. Table 6.6 Bone density values of Rangifer tarandus (Lam et al. 1999) compared to %NNISP and %MAU values for white-tailed deer long bone portions in the Middle Preclassic Pacbitun assemblages. Bone portion Humerus proximal shaft distal Radius proximal shaft distal Ulna proximal shaft Metacarpal proximal shaft distal Femur proximal shaft distal Tibia proximal shaft distal Metatarsal proximal shaft distal Scan site HU1 HU3 HU5 RA1 RA3 RA5 UL1 UL2 MC1 MC3 MC6 FE1 FE4 FE6 TI1 TI3 TI5 MR1 MR3 MR6 Density (g/cm3) 0.26 1.12 0.48 0.53 1.09 0.49 0.49 0.84 0.92 1.10 0.68 0.52 1.15 0.32 0.35 1.13 0.73 0.90 1.08 0.59 %NNISP 0.0 100.0 37.5 25.0 37.5 0.0 37.5 37.5 75.0 81.3 18.8 12.5 62.5 62.5 25.0 50.0 12.5 37.5 43.8 18.8 %MAU 0.0 100.0 50.0 33.3 33.3 0.0 33.3 50.0 83.3 100.0 16.7 16.7 66.7 83.3 33.3 50.0 16.7 33.3 50.0 16.7 Using Spearman’s rank order correlation coefficient (rs), both %NNISP and %MAU values are positively and significantly correlated with reindeer bone density values (%NNISP rs = 0.61, p = 0.004; %MAU rs = 0.52, p = 0.02) (Figures 6.2 and 6.3). These results suggest that the densest bone portions (shafts) of white-tailed deer were recovered more frequently than the less dense bone portions (epiphyses) from the same bones. Therefore, a destructive agent or process has probably affected the recovery of deer skeletal elements in the Pacbitun assemblages. It should be noted, however, that 107 120 rs = 0.61, p = 0.004 100 sHUM sMTC %NNISP 80 pMTC sFEM dFEM 60 sTIB 40 pULN dHUM sULN pRAD dMT pTIB 20 dMC pFEM pHUM 0 0.00 sMT sRAD pMTT dTIB dRAD 0.20 0.40 0.60 0.80 1.00 1.20 Density (g/cm3) Figure 6.2 %NNISP of long bone portions of white-tailed deer versus bone density values (g/cm3). Data from Table 6.6. Abbreviations: p = proximal; s = shaft; and d = distal. 120 rs = 0.52, p = 0.02 100 sMC sHUM %MAU pMC dFEM 80 sFEM 60 40 pTIB 20 sTIB sULN dHUM pULN sMT pMT pRAD sRAD dMC pFEM dTIB dMT 0 0.00 pHUM 0.20 dRAD 0.40 0.60 0.80 1.00 1.20 Density (g/cm3) Figure 6.3 %MAU of long bone portions of white-tailed deer versus bone density values (g/cm3). Data from Table 6.6. Abbreviations: p = proximal; s = shaft; and d = distal. 108 19.8% of the indeterminate portion of the assemblages is made of spongy bone. Therefore, cancellous bone has not disappeared from the assemblages. Instead, it is proposed that skeletal elements and element portions of low density have been fragmented by destructive processes to the extent that spongy specimens have become analytically absent from the samples (Lyman and O'Brien 1987; Morin 2010). Differential preservation caused by bone density may not only affect skeletal part representation, but also the taxonomic composition of faunal assemblages. Unfortunately, it was not possible to perform analyses of bone density on smaller taxa due to small sample size and/or lack of bone density values. In sum, the analysis of density-mediated attrition at Pacbitun simply indicates a correlation between bone density and element frequency. In order to identify the attritional agent(s) responsible for the destruction of spongy bones, the subsequent sections discuss bone burning, post-depositional destruction, and carnivore ravaging. 6.2.4 Bone burning Because bones tend to become more friable as burning intensity increases (Stiner et al. 1995), it is necessary to assess the impact of burning on the Pacbitun material. At Pacbitun, only a fraction of the assemblages (2.2%, n = 38) is affected by burning. Burned bones are small, with no specimen larger than 4 cm. In fact, the majority (65.8%) are smaller than 2 cm. Although fragmentation might have affected bone identification, given that most burned bones are unidentified specimens, no difference in level of fragmentation was found between the burned and unburned portions of the assemblages (D = 0.17, p = 0.999). 109 Interestingly, none of the burned remains in the Pacbitun assemblages are from spongy bone. Many authors (e.g., Villa et al. 2004; Morin 2010) have argued that the preponderance of burned spongy bone in a faunal assemblage may be indicative of the use of bone as fuel. In contrast, cortical and spongy bone should be recovered in similar proportions if burning was used as a way to dispose of food waste (Clark and Ligouis 2010). Given the absence of burned spongy bone at Pacbitun, it seems unlikely that bone was used as fuel at the site. Overall, the low frequency of burned specimens seems inconsistent with burning as a major taphonomic agent in the Middle Preclassic assemblages at Pacbitun. 6.2.5 Post-depositional destruction In order to assess the impact of post-depositional destruction, Marean (1991) has proposed a completeness index which estimates the fragmentation of small, compact elements, including the carpals, tarsals (with the exception of the calcaneus), lateral malleolus, and sesamoids. These bones were chosen by Marean because they are rarely fragmented by humans or carnivores for the extraction of nutrients. In rare instances, they may be fragmented for bone grease production (Binford 1978:164–165). These bones may also be swallowed by carnivores, but this does not seem of great concern at Pacbitun given that no digested remains were identified in the assemblages. Villa and colleagues (2004) recommended the inclusion of the third phalanx in the index, because it should be more sensitive to post-depositional breakage given the small marrow cavity of this element. Following Villa and colleagues (2004), compact elements were coded as complete (CO), almost complete (ACO), or fragmented (FR). Bones with traces of percussion, chopping, or gnawing/digestion were excluded from the sample because their 110 fragmentation may not result from post-depositional destruction (Marean 1991). Both white-tailed deer and red brocket deer specimens were considered in the analysis. The results of the completeness index (Table 6.7) may suggest that postdepositional breakage has not significantly altered the Middle Preclassic assemblages. Indeed, the majority of the compact bones from both the early (66.7%) and late Middle Preclassic (75.0%) samples are complete or almost complete. Nevertheless, the percentages also indicate that post-depositional breakage is responsible for at least some bone fracturing at the site. It should be noted that the index is influenced by the degree of identification of the remains. More complete specimens are easier to identify than fragmented ones, which may inflate the index of completeness. As a result, additional methods are required to assess the impact of post-depositional destruction on faunal assemblages. Table 6.7 Degree of post-depositional completeness by time period. Time period early Middle Preclassic late Middle Preclassic Total Total compact bones 15 20 35 NISP CO+ACO 10 15 25 %CO+ACO 66.7 75.0 71.4 Villa and colleagues (2004) argue that a high proportion (~70%) of green-bone fractures on long bones, combined with high values for the completeness index, is indicative of minimal post-depositional destruction. At Pacbitun, all long bone fragments from identified and indeterminate medium and large mammals were considered for analysis. Recent breaks were not included for obvious reasons. In the Pacbitun Middle Preclassic samples, green-bone fractures are more common than dry-bone fractures, forming 69.8% (n = 104) of the assemblages (Table 6.8). The differences in the 111 frequencies of green-bone and dry-bone fractures between the early and late Middle Preclassic samples is not statistically significant (χ2 = 0.01, p = 0.91). Table 6.8 NISP counts for green- and dry-bone fractures by time period. Fracture type Green-bone Dry-bone Total early Middle Preclassic n % 36 69.2 16 30.8 52 100.0 late Middle Preclassic n % 68 70.1 29 29.9 97 100.0 Total n % 104 69.8 45 30.2 149 100.0 The high frequency of fractures on green bone, as well as the results of the completeness index, is indicative of limited post-depositional breakage. It also suggests that a majority of long bone specimens were likely fractured before the deposition of the assemblages. To determine which agent is responsible for bone fracturing at Pacbitun, anthropic and carnivore activity at the site are discussed in the remainder of this chapter. 6.2.6 Bone surface preservation Marks left on bones by carnivores and humans are critical for inferring the role of these two agents on assemblage formation, but surface damage may alter the presence of marks on faunal specimens. Therefore, before discussing anthropic and carnivore attrition, it is necessary to assess the preservation of bone surfaces at Pacbitun. The preservation of the faunal remains ranges from poor to moderate (Table 6.9). A majority of specimens (69.6%) display a poorly preserved surface, with few bones (0.9%) considered as intact. This pattern is not unusual at Maya sites given that organic remains in the humid tropics do not appear to preserve well (Stanchly 2004; Wake 2004a). For instance, Emery (1997:315) reported that bone surfaces in the Petexbatun assemblages were highly eroded and, in many cases, had entirely disappeared. 112 Table 6.9 Overall surface state for the Middle Preclassic Pacbitun assemblages. Preservation state Poor Damaged Slightly damaged Intact Total early Middle Preclassic n % 302 53.4 158 27.9 98 17.3 8 1.4 566 100.0 late Middle Preclassic n % 902 77.5 168 14.4 87 7.5 7 0.6 1164 100.0 Total n 1204 326 185 15 1730 % 69.6 18.8 10.7 0.9 100.0 The percentage of undamaged surface area was also recorded for all faunal specimens (Table 6.10). Each category of observable surface is represented in the two samples, but a majority of specimens are in damaged or poor condition. Fifty-five percent of the assemblages are characterized by a preserved surface area lesser than 20% of the initial bone surface, whereas only 12.9% have retained more than 60% of the original surface. This poor to moderate surface preservation may be partially attributed to the effects of weathering, given that exfoliation and root etching were observed on 94.7% and 21.3% of the fragments, respectively. Other less common alterations include staining (6.2%), cracking (3.8%), and sheeting (1.0%). Overall, comparison of bone surfaces for the two samples suggests that the late Middle Preclassic material was more severely damaged by taphonomic processes than the early Middle Preclassic material. This is confirmed by statistical tests, given that differences in frequencies between the early and late Middle Preclassic samples are highly significant for both the overall surface condition (χ2 = 106.0, p < 0.0001) and the percentage of observable surface (χ2 = 174.5, p < 0.0001). The significant damage caused to the bone surfaces limited the taxonomic identification of the material, particularly long bone shaft fragments, by destroying 113 Table 6.10 Percentage of observable surface in the Middle Preclassic samples. Observable surface % 0–10 10–20 20–30 30–40 40–50 50–60 60–70 70–80 80–90 90–100 Total early Middle Preclassic n % 22 3.9 87 15.4 90 15.9 109 19.3 85 15.0 59 10.4 53 9.4 24 4.2 19 3.4 18 3.2 566 100.0 late Middle Preclassic n % 175 15.0 411 35.3 166 14.3 135 11.6 115 9.9 53 4.6 47 4.0 22 1.9 20 1.7 20 1.2 1164 100.0 Total n 197 498 256 244 200 112 100 46 39 38 1730 % 11.4 28.8 14.8 14.1 11.6 6.5 5.8 2.7 2.3 2.2 100.0 muscle attachments and landmarks. Similarly, the poor surface preservation possibly hindered the identification of marks. Because of their faint nature, cutmarks may have been partly or entirely obliterated on a significant portion of the assemblages. Cutmarks were identified on only eight specimens at Pacbitun and were observed almost exclusively on specimens displaying a slightly damaged or damaged surface (Table 6.11). An increase in cutmark frequency from the slightly damaged to damaged categories may indicate that these two categories of objects have possibly not been affected by surface damage to the same extent as the other two groups. The presence of only one specimen in the poor category, given that nearly half of the sample (49.3%) presents a poorly preserved surface, suggests that the total frequency of cutmarks may be somewhat underestimated in the assemblages. Taking these observations into consideration, the final section of this chapter examines the role of human and carnivore agents in the formation of the Pacbitun assemblages. 114 Table 6.11 Frequencies of cutmarks on identified specimens and indeterminate long bone shafts by overall surface state for the Middle Preclassic samples at Pacbitun. Preservation state Poor Damaged Slightly damaged Intact Total n 213 117 94 8 432 ncut 1 5 2 0 8 %cut 0.5 4.3 2.1 0.0 1.9 6.2.7 Human and carnivore agents A priori, the Pacbitun faunal assemblages have been produced primarily by human activity. Most of the material was recovered inside or within the periphery of domestic structures (see Table 6.1) and found in association with ceramics, lithic tools, and shell beads (Arendt et al. 1996; Hohmann and Powis 1996, 1999; Hohmann et al. 1999; Powis 2009, 2010, 2011). Faunal remains recovered in secondary contexts (i.e., secondary midden, plaza fill, and construction fill) were also found with important quantities of domestic refuse. However, given the presence of domesticated dogs at Maya sites during the Middle Preclassic period (Pohl 1990; Shaw 1991; Wing and Scudder 1991; Clutton-Brock and Hammond 1994; Masson 2004a), this species may have modified or contributed to the faunal assemblages. Other carnivores, such as felines, mustelids, and procyonids, also have the ability to alter and accumulate bone assemblages (Andrews and Evans 1983; Seymour 1989; Martín and Borrero 1997; Álvarez et al. 2012). The presence of cutmarks, percussion notches, and burning on bone specimens (Table 6.12) indicate that humans were involved in the formation of the Pacbitun faunal assemblages. Very few cutmarks (n = 8) were observed on the faunal specimens, but, as previously mentioned, this is likely the result of the generally poor preservation of bone 115 surfaces. This pattern seems typical of Maya sites, given that cutmarks are frequently identified on less than 1% of the faunal assemblages (e.g., Hamblin 1984:184–185; Carr 1986:293; Pohl 1990:157; Shaw 1991:226; Emery 1997:315). The cutmarks identified at Pacbitun were found on the following skeletal elements: white-tailed deer femur (n = 1), white-tailed deer calcaneus (n = 1), white-tailed deer naviculocuboid (n = 1), white-tailed deer rib (n = 1), jaguar phalanx (n = 1), turtle shell fragment (n = 1), and mammal long bone fragments (n = 2). Table 6.12 Frequencies of anthropogenic marks observed in the Middle Preclassic Pacbitun assemblages. Time period early Middle Preclassic late Middle Preclassic Total n* 7 1 8 Cutmark total1 178 254 432 % 3.9 0.4 1.9 Percussion notch n* total1 % 0 178 0.0 4 254 1.6 4 432 0.9 n 11 27 38 Burning total 566 1164 1730 % 1.9 2.3 2.2 * n represents the number of specimens displaying at least one cutmark or percussion notch. 1 the total includes identified specimens and indeterminate long bone shafts only. Burned bones, an unambiguous marker of anthropogenic activity, are rare at Pacbitun, representing only 2.2% of the total assemblages. Similar percentages were observed at Copán (2.6%; Collins 2002), while other Maya sites present higher values ranging from 5–16% (e.g., Hamblin 1984:185; Carr 1986:304; Shaw 1991:227; Emery 1997:315). Most of the burned bones in the Pacbitun assemblages are of brown or black color suggesting fires of moderate temperatures (Nicholson 1993; Stiner et al. 1995). White or blue bones, more likely indicative of higher fire temperatures (Nicholson 1993; Stiner et al. 1995), were rarely encountered. This observation applies to both the identified and indeterminate portions of the assemblages. 116 The presence of notches was recorded during the analysis. However, due to overlap in notch morphologies produced by humans and carnivores (Capaldo and Blumenschine 1994; Galán et al. 2009), they were not strictly considered diagnostic of human action. None of the four observed percussion notches were associated with gnaw marks at Pacbitun, which might suggest that these were produced during marrow cracking. Combined with the above reservations, percussion notches are presented along with cutmarks and burning as possible evidence of human involvement in assemblage formation. Carnivore remains are rare at Pacbitun, forming only 3.8% of the assemblages (n = 11, see Table 6.4). No single species dominate this group composed of dogs, coatis, weasels, and various large and small felines. One specimen, a jaguar phalanx, shows cutmarks, perhaps indicative of skinning. This suggests that at least some carnivore specimens were accumulated by the Maya. Gnawing marks (e.g., tooth pits, punctures, furrows, etc.) affect only 1.9% of the assemblages (Table 6.13). These results are similar to those observed at Colha and Cozumel, where carnivore marks were identified on 1.2% (Shaw 1991:244) and 2.0% (Hamblin 1984:186) of the total assemblage, respectively. However, the frequency of carnivore-modified bones increases to 6.5% when unidentified specimens are excluded. The low incidence of carnivore marks in the indeterminate portion of the assemblages may be caused by increased fragmentation, most unidentified specimens (84.8%) being no longer than 2 cm. Surface preservation might also be responsible for this pattern, considering that the majority of small indeterminate specimens have a poorly preserved surface. 117 Table 6.13 Frequencies of carnivores marks observed in the Middle Preclassic Pacbitun assemblages. Time period early Middle Preclassic late Middle Preclassic Total n 14 19 33 Gnawing total 566 1164 1730 % 2.5 1.6 1.9 n 0 0 0 Digestion total 566 1164 1730 % 0.0 0.0 0.0 No traces of digestion or rodent marks were identified. Given the high level of fragmentation and the poor to moderate preservation of the Pacbitun faunal assemblages, it is possible that the digested remains did not survive at the site. As a matter of fact, digested specimens are more vulnerable to taphonomic processes than intact specimens because of the corrosion caused by gastric acids (Holwitz 1990). Therefore, their frequency may be slightly underestimated at Pacbitun, although digested bones do not seem common at Maya sites (Shaw 1991:244). A qualitative assessment of the extent of gnawing on bone surfaces suggests that carnivore ravaging was limited at the site (Table 6.14). Most carnivore marks were coded as marginal (75.8%), meaning that they were uncommon on the bone surface. They appear almost exclusively on spongy bones, such as the vertebrae and epiphyses of long bones. This pattern is expected given that carnivores are primarily attracted to greasy bone parts. It also suggests that carnivores may be responsible to some extent for the fragmentation of spongy bone observed at the site. Overall, the data on cutmarks, percussion notches, and burning suggests that most of the remains at Pacbitun were brought to the site and processed by humans. The low incidence of gnawing marks and digested remains probably indicates that carnivores contributed minimally to the bone assemblages and did not significantly modify 118 Table 6.14 Extent of carnivore gnawing on bone surfaces for the Middle Preclassic samples at Pacbitun. Time period Marginal early Middle Preclassic late Middle Preclassic Total n 11 14 25 % 78.6 73.7 75.8 Limited to one section n % 2 14.3 2 10.5 4 12.1 Covered n 1 3 4 % 7.1 15.8 12.1 Total n 14 19 33 % 100.0 100.0 100.0 the material. In fact, it seems reasonable to argue that carnivores, domestic dogs in particular, had secondary access to faunal remains after these had first been exploited by humans. The combined presence of cut and gnaw marks on a white-tailed deer femur (PAC-97BO-002) seems to support this idea (Figure 6.4). Several punctures and tooth pits were observed on the lateral condyle of the distal end of the femur, whereas a set of cutmarks were identified in the intercondylar fossa. Figure 6.4 Gnaw and cut marks on the distal end of a right white-tailed deer femur. On the left: two cutmarks in the intercondylar fossa. On the right: view of the lateral condyle with gnawing marks. 0 1 cm 0 1 cm 119 Prey size may also constitute an argument in favor of this hypothesis. Indeed, the majority of gnaw marks (28/33, 84.8%) were found on bones of large mammals, such as white-tailed deer, red brocket deer, and peccary. However, most carnivores present in the Maya subarea, with the exception of large felines, do not prey on animals of this size. Studies have even shown that dogs are rarely successful in catching and killing deer (Marchinton 1994). Therefore, it is most likely that carnivores modified assemblages first created by human activity. Nevertheless, the possibility that carnivores may have contributed sporadically to the assemblages, particularly by introducing smaller taxa such as rabbits, agoutis, and opossums, cannot be ruled out. 6.2.8 Taphonomy of fish and birds Up to this point, this chapter has mainly focused on the impact of taphonomic processes on mammalian remains, the most common taxonomic class identified at Pacbitun. This is not surprising given that mammals form 96.8% of the Pacbitun assemblages. However, under comparable depositional circumstances, remains of birds and fish may not behave in a manner similar to mammal remains. As a result, this section discusses the taphonomic history of fish and bird specimens recovered in the Middle Preclassic assemblages at Pacbitun. Fish and bird bones are generally considered less robust than mammalian bones (Lyman 1994; Higgins 1999). For instance, actualistic research has shown that bird and fish specimens have a tendency to weather more rapidly than mammal remains (e.g., Nicholson 1996; Behrensmeyer et al. 2003; Cruz 2008). Fish remains are sensitive to the action of gastric acids and acidic soils, particularly if they have been boiled or moderately burned (Wheeler and Jones 1989; Butler 1990; Lubinski 1996). Because of their thin 120 cortical surface, bird bones may be easily fragmented and even destroyed by carnivore ravaging (Dirrigl 2001; Cruz 2008; Serjeantson 2009), although they might appear less attractive to carnivores than mammal bones as a result of their low marrow content (Serjeantson 2009). It is also considered difficult to identify evidence of cultural modifications on avian remains (Dirrigl 2001). Cutmarks are generally more difficult to recognize on small- and medium-sized birds, because cutting or chopping implements may not be needed to disarticulate small skeletons. Birds of small size may also not need to be butchered because they can be cooked whole. Such practice would not leave any marks on the bones (Serjeantson 2009). Similar to mammalian bone, some elements of bony fishes tend to preserve better than others. Cranial elements are generally considered to weather faster than vertebrae (Butler 1990; Butler and Chatters 1994; Lubinski 1996), with the exception of teeth and otoliths, which are some of the most durable elements of fish (Butler and Chatters 1994). It is important to note that fish of different families may not be affected by taphonomic processes to the same degree as a result of differences in the size, shape, and density of their skeleton (Wheeler and Jones 1989; Butler and Chatters 1994; Lubinski 1996; Butler and Schroeder 1998). Concerning birds, bone density has been recorded using different methods (e.g., Higgins 1999; Dirrigl 2001; Broughton et al. 2007), but the ranking of skeletal elements from densest to least dense is inconsistent between different studies. In general, thin and flat bones, such as the sternum and skull, are considered more fragile than long bones (Serjeantson 2009). Different criteria may be combined in order to distinguish between culturally and naturally deposited assemblages of fish (Butler 1993; Zohar et al. 2001) and birds (Serjeantson 2009), including taxonomic diversity, specimen size, bone structural density, 121 skeletal element representation, spatial distribution of the remains, and presence of burning and cutmarks. Due to the small size of both fish (n = 8) and bird (n = 5) samples at Pacbitun, these methods could not be applied. The fish remains are mostly represented by centrum fragments which lack spines. This considerably limited identification. One bird remain is identified as the fibula of a Galliform, whereas other specimens consists of three long bone fragments and one sternum fragment. None of the fish or bird remains display traces of human or carnivore modification. All fractures on bird long bones were identified as dry-bone fractures or were classified as ambiguous. Because of the small size of the fish and bird samples and the absence of carnivore or anthropic marks on them, it is difficult to be conclusive about their mode of introduction in the Pacbitun assemblages. It is possible that the low frequency of small birds and fish was caused by differential preservation of these remains over time. It is possible that fish and bird remains were affected by taphonomic processes to a greater extent. They also might have been discarded elsewhere at the site (Emery 2004a, 2008b). For instance, the discovery of pits filled with fish at Colha led Shaw (1991:238) to suggest that fish may have been buried quickly and separately from other food refuse. The presence of domestic dogs at Pacbitun may also have decreased the probability of recovering fish and bird specimens because these may have been deleted from the assemblages by carnivores. Finally, these small species may also be absent simply because they were rarely exploited by the ancient Maya. 6.3 Summary This chapter has shown that the Middle Preclassic assemblages at Pacbitun have been shaped by several taphonomic processes. The use of different recovery methods 122 does not seem to have affected the taxonomic composition of the assemblages. In comparison, weathering has altered a majority of faunal remains. This situation has significantly impeded the identification of the material. It is suggested that fragmentation of spongy bone may have been caused by carnivore ravaging of human-accumulated debris, some post-depositional destruction, and perhaps burning. Humans were likely responsible for the accumulation of most remains in the Middle Preclassic samples, although carnivores possibly contributed and modified a small portion of the assemblages. Overall, the extent of bone surface damage seems to be the only taphonomic process that has affected the early and late Middle Preclassic samples differently. The next chapter examines the subsistence strategies associated with the exploitation of animal resources at Pacbitun. 123 CHAPTER 7: RESULTS This chapter examines how the ancient Maya of Pacbitun utilized animal resources during the Middle Preclassic period. The chapter first begins with a description of the assemblages in terms of taxonomic composition, skeletal part representation, mortality profiles, and seasonality. Using the central place foraging prey choice model presented in Chapter 4, this chapter investigates the foraging strategies adopted by the Pacbitun Maya. Finally, the findings of this study are compared with the subsistence patterns observed at other Middle Preclassic sites. 7.1 Taxonomic composition Species abundances in the Pacbitun assemblages are presented using NISP counts. MNI counts were not used in this study because of small sample size. A highly significant correlation between NISP and MNE values (early Middle Preclassic rs = 0.95, p < 0.001; late Middle Preclassic rs = 0.90, p < 0.001) also suggests that the ranking of identified species provided by these two quantification methods are similar. Therefore, the use of both methods in the presentation of taxonomic composition would be redundant. The Middle Preclassic assemblages at Pacbitun are quite diverse given their small size (less than 170 identified specimens per time period). The early Middle Preclassic assemblage is represented by 18 different taxa, while 21 taxa were identified in the late Middle Preclassic sample (Table 6.4). The early Middle Preclassic assemblage is dominated by white-tailed deer (40.8%). Other ungulates, namely the red brocket deer and peccary, comprise 5.6% and 4.8% of the sample, respectively. In the early Middle Preclassic sample, most specimens identified as large mammals (n = 39) are also presumed to be from white-tailed deer. Although many of these specimens are long bone 124 shafts and rib fragments lacking diagnostic features, they present characteristics, such as size and density, that are consistent with that of white-tailed deer elements. The armadillo (13.6%) and turtles (8.8%) also form a significant portion of the assemblage. However, it should be noted that the use of NISP counts may overestimate the importance of these two taxa in the present case. Indeed, both species have a very large number of bones as a result of the shells that form their carapace (Emery 2007b). These bony scutes tend to preserve well and are highly diagnostic (Soibelzon et al. 2012). While carapace or plastron fragments constitute the majority of identified turtle specimens, the armadillo is mainly represented by long bone fragments. The armadillo also produced the second highest MNE (n = 13), which may suggest that it was an important small game for the Pacbitun Maya. Other small game include large rodents (agouti and paca), which collectively represent 4.8% of the sample, and the pocket gopher (3.2%). Rare species (less than 2% of the assemblage) include the Virginia opossum, rabbit, iguana, colubrid snake, and all carnivores (i.e., domestic dog, coatimundi, jaguar, and ocelot). Fish remains are also not abundant (6.9%). Two specimens were attributed to the Ictaluridae (freshwater catfish) and Serranidae (grouper) families. Similarly, bird remains are infrequent (1.6%) and could not be identified more precisely than the class level. The late Middle Preclassic assemblage is similar in composition to the early Middle Preclassic (Kolmogorow-Smirnov D = 0.21, p = 0.74). The white-tailed deer is the most common taxon, representing 52.7% of the sample. It is followed by the armadillo (10.8%), red brocket deer (6.0%), and peccary (4.2%). Like the early Middle Preclassic sample, most remains identified as large mammals (n = 65) are probably from white-tailed deer. Turtles are much less common in this sample (3.6%). One specimen 125 was identified as a mud turtle, while most of the other specimens are heavily weathered, poorly diagnostic carapace fragments. The proportion of rodents is also lower in the late Middle Preclassic assemblage, with agouti and pocket gopher representing only 0.6% and 1.8% of the sample, respectively. Other mammals are rare (<2%). Fish are also less common than in the early Middle Preclassic sample, with one specimen identified as a parrotfish and another only identified as indeterminate fish. In contrast, reptile remains are proportionately more abundant in the late Middle Preclassic assemblage (colubrid = 3.0%; viper = 1.8%; iguanas = 1.8%). Birds are again rare (1.8%), with one specimen identified as a gallinaceous bird. One marine toad was also encountered. Although the Middle Preclassic assemblages are characterized by considerable taxonomic diversity, the following discussion focuses principally on white-tailed deer because of small sample size. 7.2 Skeletal part representation This section describes skeletal part representation for the white-tailed deer and offers a general description of skeletal element frequencies for three other taxa: the armadillo, peccary, and brocket deer. Small sample size precluded a detailed discussion of the other identified species. Standardized NNISP counts (%NNISP) were obtained by dividing all identified elements by the highest NNISP count. %NNISP values are used because they facilitate comparisons of assemblages. MNE and MAU values are presented with NNISP counts, although they are not used in this study to investigate skeletal part representation. At Pacbitun, NNISP and MAU values show similar rankings, as is suggested by the highly significant correlation between NNISP and MAU values for 126 white-tailed deer (rs = 0.96, p < 0.001). Therefore, the use of one method over the other should result in similar interpretations. Due to small sample size, the early and late Middle Preclassic assemblages were combined in order to investigate skeletal patterns for white-tailed deer. The most common elements are mandibular and maxillary teeth, which are present in similar proportions (Table 7.1, Figure 7.1). It is not unexpected for teeth to be abundant in the samples even though the Pacbitun assemblages are poorly preserved. Teeth are among the densest skeletal elements (Reitz and Wing 2008:46) and can be easily distinguished from bone Maxillary teeth Mandibular teeth Atlas Axis Cervical vertebrae Thoracic… Lumbar vertebrae Sacrum Rib Scapula Humerus Radius Ulna Carpals Metacarpal Innominates Femur Tibia Tarsals Metatarsal Phalanx 1 Phalanx 2 Phalanx 3 Large sesamoid 0 20 40 60 80 %NNISP Figure 7.1 White-tailed deer body part representation in the Middle Preclassic assemblages at Pacbitun. Data from Table 7.1. 100 127 Table 7.1 Skeletal part frequencies for white-tailed deer in the Middle Preclassic assemblages from Pacbitun. Bone portions not shown have a frequency of zero. Body portion Maxillary teeth Mandibular teeth Cervical vertebrae Thoracic vertebrae Lumbar vertebrae Rib Scapula Humerus, shaft Humerus, distal Radius, proximal Radius, shaft Ulna, proximal Ulna, shaft Scaphoid Lunatum Triquetrum Capitatum Metacarpal, proximal Metacarpal, shaft Innominate Femur, proximal Femur, shaft Femur, distal Tibia, proximal Tibia, shaft Tibia, distal Malleolar Astragalus Calcaneum Naviculocuboid Greater cuneiform Metatarsal, proximal Metatarsal, shaft Metapodial, shaft Metapodial, distal Phalanx 1 Phalanx 2 Phalanx 3 Large sesamoid Total NISP 8 9 2 1 1 7 1 8 3 2 3 3 3 1 1 2 1 6 5 3 1 5 5 2 4 1 3 5 6 6 4 3 2 3 3 9 8 3 5 148 NNISP 4.00 4.50 0.29 0.08 0.17 0.27 0.50 4.00 1.50 1.00 1.50 1.50 1.50 0.50 0.50 1.00 0.50 3.00 2.50 1.50 0.50 2.50 2.50 1.00 2.00 0.50 1.50 2.50 3.00 3.00 2.00 1.50 1.00 0.75 0.75 1.13 1.00 0.38 0.31 %NNISP 88.9 100.0 6.3 1.7 3.7 6.0 11.1 88.9 33.3 22.2 33.3 33.3 33.3 11.1 11.1 22.2 11.1 66.7 55.6 33.3 11.1 55.6 55.6 22.2 44.4 11.1 33.3 55.6 66.7 66.7 44.4 33.3 22.2 16.7 16.7 25.0 22.2 8.3 6.9 MNE 3 4 2 1 1 5 1 6 3 2 2 2 3 1 1 2 1 5 5 2 1 4 5 2 3 1 3 4 5 5 4 2 2 2 2 6 7 3 5 118 MAU 1.50 2.00 0.29 0.08 0.17 0.19 0.50 3.00 1.50 1.00 1.00 1.00 1.50 0.50 0.50 1.00 0.50 2.50 2.50 1.00 0.50 2.00 2.50 1.00 1.50 0.50 1.50 2.00 2.50 2.50 2.00 1.00 1.00 0.50 0.50 0.75 0.88 0.38 0.31 %MAU 50.0 66.7 9.5 2.6 5.6 6.4 16.7 100.0 50.0 33.3 33.3 33.3 50.0 16.7 16.7 33.3 16.7 83.3 83.3 33.3 16.7 66.7 83.3 33.3 50.0 16.7 50.0 66.7 83.3 83.3 66.7 33.3 33.3 16.7 16.7 25.0 29.2 12.5 10.4 fragments even when heavily weathered. The rest of the sample is dominated by long bones, with shaft fragments being slightly more common than epiphyses. As discussed in 128 Chapter 6, this situation probably results from mediated-density attrition. The humerus is the most common long bone, followed by the metacarpal and femur. Tarsals, and to a lesser extent carpals and phalanges, are also abundant. Cranial elements and mandibles are only represented by loose teeth. Elements of the axial skeleton, such as vertebrae and ribs, are rare in the assemblages. The under-representation of these elements may result from differential preservation, as elements of low structural density are less frequent in the assemblages than elements of higher density. The peccary and red brocket deer have a respective NISP of 13 and 17 (Table 7.2). As for the white-tailed deer, elements of the axial skeleton are poorly represented in these species. Long bone specimens are well represented for the brocket deer (7/17, 41.2%), but Table 7.2 Skeletal part frequencies (NISP) of armadillo, peccary, and red brocket deer for the Middle Preclassic period at Pacbitun. Bone portions that are not listed have a frequency of zero. Body part Armadillo Peccary Brocket deer Maxillary teeth 1 Cervical vertebrae 1 Scapula 1 Humerus 1 Radius 2 2 Ulna 1 1 Carpals 3 Metacarpal 1 2 Femur 2 1 Tibia 10 1 Fibula 2 Tarsals 2 2 2 Metatarsal 1 2 Phalanx 1 1 3 4 Phalanx 2 3 Phalanx 3 1 Scute 12 Total 35 13 17 129 not as abundant for the peccary (3/13, 23.1%). Phalanges, carpals, and tarsals are most common in these species (peccary = 8/13, 61.5%; brocket deer = 10/17, 58.8%). The armadillo is primarily represented by bony scutes (12/35, 34.2%). This pattern is not surprising given that these elements are highly diagnostic. Long bones are also frequent, particularly the tibia (10/35, 28.6%). 7.3 Mortality profiles As it is the case for most faunal assemblages recovered from Maya sites, data concerning prey age and sex is very limited in the sample. Osteometric measurements could not be applied in this study due to the highly fragmented nature of the specimens. It should be noted that the usefulness of osteometric data in the tropics may be limited to few animals, including white-tailed deer, because many mammal species present in the study region, such as the peccary, rabbit, or agouti, do not exhibit any apparent or only show weak sexual dimorphism (Ojasti 1996). Antlers may also provide coarse information on the sex and age composition of an assemblage. Unfortunately, antler remains are absent from the Pacbitun samples. This pattern may have several causes. For instance, the Preclassic Maya may have preferentially used crania (with attached antlers) for decorative and ritual purposes, for instance in the making of headdresses (Pohl 1981; Brown and Sheets 2000) or as offerings in hunting shrines (Brown 2005). Antlers may also have been left at kill sites because they are heavy to carry and possess little food value (Binford 1978). However, this observation may not apply to the present study. Because of the small size of whitetailed deer in the tropics (30–50 kg), small groups of foragers or even a single hunter may have been able to transport complete carcasses back to the site, including crania with 130 antlers. Lastly, a hunting strategy biased against male individuals could also have created this pattern. Data on age profiles was gathered from the analysis of tooth eruption and wear and epiphyseal fusion for white-tailed deer. The only tooth dated to the early Middle Preclassic was too fragmented for adequate measurement. In the late Middle Preclassic sample, two deciduous teeth were available for analysis. The first one is a lower fourth premolar. Crown height measurement, combined with the absence of dental wear, suggests an age of less than seven weeks (Severinghaus 1949). The second deciduous tooth is also a lower fourth premolar, which exhibits considerable wear. The age of this individual is estimated between 17–20 months, falling within the subadult category (1–2 years old) (Severinghaus 1949; Gee et al. 2002). The number of permanent teeth adequately preserved for crown height measurements is also relatively small. Three specimens are classified as subadults: two lower first molars correspond to an age at death of 20–26 months, whereas one second lower molar exhibiting little wear provides an age of about 13–14 months (Severinghaus 1949). Only one tooth, a lower third molar, is classified as pertaining to an adult (>2 years old). The presence of little to no wear (Gee et al. 2002) suggests the presence of a young individual. No completely worn teeth were identified in the Middle Preclassic assemblages, suggesting the absence of old and very old individuals. Although it may only provide coarse information on mortality profiles, the age of white-tailed deer specimens was also determined using sequences of epiphyseal fusion (Purdue 1983). The main drawback of this method is that it does not allow to extrapolate the age of an individual passed the time of bone fusion. For the early Middle Preclassic sample, 19 bones were analyzed (Table 7.3). From these, three specimens show unfused 131 epiphyses. The identification of these unfused bone portions indicate the presence of young individuals (<2 years old) in the assemblage. The presence of four fused first phalanges, which are completely fused between 17–20 months of age, indicates that subadults and adults may have been taken. Finally, ten out of nineteen specimens are element portions which are completely fused between 26–38 months of age. This suggests that about half of the specimens in the sample are from adult individuals. Table 7.3 Number of specimens identified per category of epiphyseal fusion for whitetailed deer in the early and late Middle Preclassic samples at Pacbitun. Age of epiphyseal fusion is provided in months. Time period early Middle Preclassic (19 specimens) late Middle Preclassic (31 specimens) Element Radius, px 2nd phalanx 1st phalanx Metacarpal Ulna, px Calcaneum Femur, di Tibia, px Ulna, px Cervical vertebra, ant Radius, px Coxal 2nd phalanx Humerus, di 1st phalanx Tibia, di Metacarpal Calcaneum Metatarsal Femur, di Femur, px Unfused Intermediate Age1 n Age n 20–23 20 1 1 23–29 1 20–23 1 Fused Age1 5–8 11–17 17–20 26–29 n 1 1 4 3 26–29 26–38 26–38 26–38 38 5–8 8–11 11–17 12–20 17–20 20–23 26–29 26–29 26–29 26–38 32–38 3 1 1 1 1 1 1 7 3 5 1 2 3 3 3 1 1 Data on epiphyseal fusion in months from Purdue (1983). A range of values is provided when data for males and females differed. Abbreviations: px = proximal, di = distal, and ant = anterior. Only one specimen in the late Middle Preclassic assemblage, a distal metapodial epiphysis which generally fuses at 20 months of age, is unfused (Table 7.3). Sixteen 132 specimens are from bones which fuse between 11–23 months of age, suggesting the presence of individuals which can be considered as subadults or full adults. Twelve additional specimens are completely fused between 26–38 months of age. Therefore, 40.0% of the late Middle Preclassic specimens would belong to the subadult or young adult category. Published sequences of teeth eruption and wear are also available for the domestic dog, peccary, and paca. However, the information obtained for these taxa is very limited: no more than one or two teeth could be analyzed for each species. Based on the timing of dental eruption for collared peccary (Kirkpatrick and Sowls 1962), an upper third premolar from the early Middle Preclassic was identified as belonging to an individual at least 18 months old. However, the fact that it shows considerable wear suggests that the animal was much older. The only dog tooth identified in the samples is a lower first molar from the late Middle Preclassic period. This tooth erupts between three to five months of age (Silver 1969). Given the limited degree of wear observed on the cusps, the tooth is attributed to a juvenile individual. In the case of the paca, the presence of intact folds on a lower first molar, which become isolated early in the wear sequence (Ungar 2010:215), suggests a very young individual. Another paca tooth was identified as a lower third molar. Although this tooth erupts at about 14 months of age (Oliveira and Canola 2007), the heavy wear and isolated folds indicate a much older individual. These two teeth date to the early Middle Preclassic period. Overall, data on tooth wear and epiphyseal fusion for white-tailed deer suggests that the Pacbitun Maya focused on the exploitation of subadults and young adults. Very old individuals appear to have been absent in the assemblages. However, this pattern may be an artefact of small sample size, given that only six teeth were available for analysis. 133 There is also limited evidence for the exploitation of very young individuals. However, it should be noted that unfused epiphyses, as well as deciduous teeth, are more vulnerable to the action of post-depositional destruction or carnivore ravaging than completely formed bones or teeth (Klein and Cruz-Uribe 1984:43). Given that the Pacbitun assemblages have been affected to some degree by these two processes, very young individuals may be under-represented because of differential preservation. 7.4 Scheduling of activities The Middle Preclassic residents of Pacbitun occupied a landscape which was spatially and seasonally diverse. Given that they largely subsisted on agriculture, the ancient Maya would have had to integrate animal resource procurement into the scheduling of agricultural activities throughout the year. Ethnographic accounts suggest that swidden agriculture, the type of agriculture which is believed to have been practiced at Pacbitun during the Middle Preclassic (Healy et al. 2004b), was more likely carried out during the wet season, although wetlands can also be cultivated during the dry season (Pohl 1990:155). Given that most species in the tropics can breed year-round, or have birthing peaks extending over several months (Chapter 4), it was not possible to determine the season of capture of the species identified at Pacbitun. This situation inhibited insights regarding activity scheduling. 7.5 Diet breadth The investigation of diet breadth can provide information about past foraging efficiency and animal procurement strategies. At Pacbitun, diet breadth was examined by comparing taxonomic abundances using the prey ranks presented in Chapter 4. According to the body size rule (Figure 4.1), the tapir should be considered the highest-ranked prey 134 type. At Pacbitun, this animal is only represented by a single specimen. Following the predictions of the central place forager prey choice model, it is suggested that the scarcity of tapir possibly reflects a decline in the abundance of this animal in patches located near the site. Consequently, the residents of Pacbitun should have invested more time in searching for and handling resources ranked lower on the body mass scale (see discussion about artiodactyls). It is also possible that this animal was infrequently encountered because of its behavioral habits. Indeed, tapirs are solitary animals, which travel extensively and prefer to live in the dense, low vegetation of mature forests. In fact, this animal is seldom encountered at Maya sites. Ethnohistoric and ethnographic accounts report that the tapir is not usually taken by the Maya; it is either regarded as too difficult to kill and transport (Tozzer 1941:203; Jorgenson 1999) or as non-edible (Hopkins 1992; Fry 2009). The jaguar and puma occupy the second and third ranks on the body mass scale (Figure 4.1). Although predatory defense mechanisms make carnivores dangerous to exploit in comparison to the relatively docile white-tailed deer, tapir, or peccary, this parameter may explain why felines would have been taken by the Maya. Indeed, pursuing large, high-risk animals may not always be the most profitable activity in terms of return rates, but it can confer prestige onto hunters (McGuire and Hildebrandt 2005; Lupo 2007). At Pacbitun, felines are not abundant in the Middle Preclassic assemblages (early Middle Preclassic = 2.4% of NISP, late Middle Preclassic = 1.8%). However, carnivores are generally encountered less frequently than herbivores as a result of their high rank in the trophic chain. Evidence from the Classic period suggests that bones of large felines were used in the manufacture of objects (Moholy-Nagy 1994; Emery 2008a, 2009) and that their skins 135 and teeth were worn by priests and rulers as a symbol of their high social status (Pohl 1983; Hopkins 1992; Emery 2010). It is not known if the animals were consumed during the Classic period. Felines may have been used in a similar fashion during the Middle Preclassic. Skeletal patterns may provide evidence for the exploitation of pelts given that phalanges, metapodials, and caudal vertebrae may be left with the pelt when fur-bearing animals are skinned (Fairnell 2008; Reitz and Wing 2008:127). At Pacbitun, four out of six feline elements fall within this category: two phalanges from a jaguar and a small felid, one navicular from a margay, and one caudal vertebra from a small felid. Two humeri from a puma and an ocelot complete the assemblage. Although this skeletal pattern seems to point towards the exploitation of pelts, the jaguar phalanx displays three sets of deep cutmarks which probably result from the disarticulation rather than the skinning of the foot. Overall, the very small sample size of the feline assemblage makes it difficult to reach conclusions about the exploitation of these animals at Pacbitun. It seems probable that humans were involved in the accumulation of felines during the Middle Preclassic, although these taxa are only present in limited proportions at the site. Four other ungulates are also considered high-ranked resources. These are the white-tailed deer, red brocket deer, white-lipped peccary, and collared peccary. Following Emery (2008b), an abundance index was calculated to evaluate the importance of these large animals relative to smaller taxa. This “artiodactyl index” was calculated as follow: Ʃ artiodactyls / Ʃ (artiodactyls + all other mammals excluding tapir, jaguar and puma). During the early Middle Preclassic, hunting strategies seem to have focused on the exploitation of the four ungulates, as suggested by a value of 0.65 for the artiodactyl index. Higher values were observed for the late Middle Preclassic sample (artiodactyl index = 0.77), but the difference in proportions of artiodactyls between the two time 136 periods is not statistically significant (K-S D = 0.33, p = 0.97). From these four taxa, the white-tailed deer was the species most commonly targeted by the Middle Preclassic Maya. This taxon comprises 79.7% of the artiodactyl sample from the early Middle Preclassic period and 83.8% of the late Middle Preclassic artiodactyl sample. It is suggested that the Pacbitun Maya concentrated their efforts on the procurement of these four artiodactyls because higher ranked prey types were infrequently encountered. Many of the mammals of small and intermediate size, which are ranked low on the body mass scale, are rare in both the early and late Middle Preclassic samples. This pattern is, with the exception of the armadillo, in accordance with the prey ranking. It is possible that the high frequency of armadillo does not relate to the amount of meat it can procure, but rather to the amount of fat it can provide. During the wet season, armadillos build an extremely thick layer of fat relative to their body size (Hill et al. 1984; Hill et al. 1987). This characteristic could make them a desirable prey type in comparison to other small- and medium-sized mammals that tend to be much leaner. Unfortunately, the lack of quantitative data on body fat does not allow the testing of this hypothesis. Other taxa that likely violate the body size rule include turtles. These were exploited at Pacbitun, although their high frequency in the samples may be exaggerated by the use of NISP counts. Nonetheless, turtles were possibly always included in the optimal diet. As slowmoving animals, they provide important quantities of meat for little handling costs. Birds and fish seem to have been considered as resources of low profitability given that they are rare at the site. In Chapter 4, it was discussed that the en masse collection of small animals may have created rank inversions. Given the low abundance of nearly all small prey items at Pacbitun, the Middle Preclassic Maya do not appear to have invested much time in this 137 hunting strategy. Similarly, certain animals may have been preferentially targeted because their gregarious behavior increases the chances of handling multiple individuals during a foraging bout. Two species identified at Pacbitun live in large groups: the peccary and coati. Given that only one specimen of coati was identified in the samples, the gregariousness of this medium-sized animal does not appear to have modified its low ranking on the body mass scale. According to the prey ranking, the peccary is an animal of high utility at Pacbitun. Therefore, its gregarious behavior would not have affected its ranking given that it is already included in the optimal diet. The presence of snakes at Pacbitun raises the question of whether they were exploited by the Maya. Snakes are known to have been used as offerings in sacrificial ceremonies or as ornaments by the Classic period Maya (Pohl 1990; Emery 2010). They might also have been used as a source of food. Unfortunately, none of the snake specimens identified at Pacbitun present traces of anthropic activity. The presence of snakes at archaeological sites is often considered to be incidental because they are attracted to human habitations and may die there naturally. However, given that snakes are not scavengers, they do not naturally dwell in middens or refuse piles. Fradkin (2004) suggests that their presence in important quantities in this type of deposits likely result from anthropic activity. This information is crucial for the interpretation of snake exploitation at Pacbitun given that a majority of snake specimens (66.7%) were recovered in the secondary midden dating to the late Middle Preclassic period. Additionally, the size of two viper vertebrae indicates the presence of large snakes which could have provided sizeable quantities of meat. In sum, although evidence for the exploitation of snakes at Pacbitun is conjectural, it is suggested that the Middle Preclassic Maya may have intentionally captured and exploited these reptiles. 138 The only amphibian remains recovered at Pacbitun is that of a marine toad. The presence of this species in the assemblage is also difficult to interpret. It is not clear if this giant toad was eaten by the Maya because its parotoid glands produce secretions which are toxic (Campbell 1998:68). Marine toads thrive in disturbed habitats and are often found near human settlements (Campbell 1998:69). As a result, the specimen identified at Pacbitun may be intrusive or perhaps was used as poison or hallucinogenic drug. At this point, the discussion of diet breadth has focused on hunted animals. Domestic dogs are known to have been used by the Maya during the Middle Preclassic period. These animals likely served as pets and hunting companions, but evidence from sites in northern Belize suggests that they were also used as a source of food (Shaw 1991; Wing and Scudder 1991; Clutton-Brock and Hammond 1994; Masson 2004a). This practice seems unlikely at Pacbitun given that only three specimens of Canidae were recovered at the site. However, the possibility that some dogs were given a mortuary treatment different from that of other taxa cannot be discounted (Losey et al. 2011). For instance, at Cuello, dogs were recovered in special deposits and interpreted as having been used in sacrifices (Tykot et al. 1996; White et al. 2001b). Therefore, it is possible that dog remains were not frequently recovered near residential structures or in middens at Pacbitun because their remains were buried elsewhere. In summary, the taxonomic data suggests that diet breadth at Pacbitun during the Middle Preclassic was, on average, relatively narrow. Procurement of animal resources focused on white-tailed deer. Other artiodactyls were exploited in much lower proportions. The highest ranked taxa, namely the tapir, jaguar, and puma, appear to have been infrequently encountered. The available data demonstrate that a variety of lowerranked resources were also included in the diet, but their low abundances in the samples 139 suggest that they were only occasionally taken. Although the early and late Middle Preclassic samples are small in size, they both offer a similar picture of animal resource procurement (K-S D = 0.21, p = 0.74). 7.6 Habitat use The species identified in the Pacbitun vertebrate assemblages can inform us on the types of habitats exploited by the Middle Preclassic Maya. Generally, information derived from analyses of habitat use is coarse in nature because many tropical animals can thrive in a variety of habitats. The use of habitat fidelity statistics may help to overcome this limitation because values are assigned to animal species as a function of their fidelity to different types of habitats. Habitats considered in this analysis include closed canopy forest, secondary/disturbed forest, riverine/lacustrine habitats, agricultural/open areas, and residential areas (Table 7.4). In this study, the NISP count of identified species was multiplied by values of habitat fidelity obtained from Emery and Thornton (2008b). It should be noted that this analysis only includes mammalian taxa because of a lack of data and/or less precise taxonomic identification for birds, reptiles, and fish in the Pacbitun assemblages. Although these animals are excluded from the analysis of habitat fidelity, they are included in the general discussion of habitat use. The analysis of habitat fidelity suggests that the Pacbitun Maya focused their efforts on the procurement of animals which mainly thrive in secondary forests (41.3%) or agricultural fields (36.8%, Table 7.5). These results are not unexpected. At Pacbitun, the practice of swidden agriculture during the Middle Preclassic period likely resulted in the partial deforestation of the landscape. This farming strategy generally leads to the formation of areas of second growth vegetation which act as a transition between 140 undisturbed canopy forests and open cultivated areas (Emery 2010). The majority of mammals identified in the assemblages might have been attracted to this patchy environment because they can find shelter in second-growth forests during the day and visit agricultural fields and household gardens at night to feed on crops, fruit trees, and other greens. These animals include the white-tailed deer, collared peccary, and smaller game, such as the agouti, opossum, armadillo, and rabbit. Table 7.4 Habitat fidelity values for the mammalian species identified in the Middle Preclassic assemblages at Pacbitun. Values from Emery and Thornton (2008b:164). Taxon Opossum Armadillo Coatimundi Long-tailed weasel Cougar Jaguar Margay Ocelot Tapir Peccary White-tailed deer Red brocket deer Pocket gopher Paca Agouti Rabbit MF 0.1 0.2 0.35 0.4 0.4 0.65 0.6 0.5 0.2 0.6 0.1 0.6 0.45 0.25 SEC 0.5 0.4 0.4 0.4 0.4 0.2 0.4 0.3 0.2 0.5 0.3 0.5 0.5 0.3 0.5 RIV 0.2 AGR 0.4 0.2 0.2 0.2 RES 0.2 0.1 0.2 0.2 0.8 0.2 0.45 0.1 0.5 0.1 0.1 0.5 0.4 Abbreviations: MF = mature/closed canopy forest, SEC = secondary/disturbed forest, RIV = riverine or lacustrine habitats, AGR = habitats with low arboreal vegetation, including savannas and agricultural fields, and RES = residential areas. Table 7.5 Analysis of habitat fidelity for the Pacbitun assemblages, by time period. Results are provided in percentages. Time period early Middle Preclassic late Middle Preclassic Total MF 20.5 18.3 19.4 SEC 40.9 41.6 41.3 RIV 2.4 1.9 2.1 AGR 35.7 37.9 36.8 RES 0.5 0.3 0.4 Total 100.0 100.0 100.0 141 Animals which occupy closed forested areas also seem to have been acquired (19.4%), but not to the same extent as animals which thrive in disturbed habitats. This result is consistent with the low abundance of forest-dwelling animals in the assemblages, such as the white-lipped peccary, red brocket deer, paca, jaguar, margay, and tapir. These animals do not adapt well to human presence and are most commonly found in undisturbed dense forests. Therefore, the presence of these species in the Middle Preclassic assemblages suggests that hunting trips were at least occasionally taken to forested habitats. Riverine habitats do not appear to have been extensively exploited (2.1%). This is unexpected given that many secondary and tertiary water sources are available within 5– 10 km of Pacbitun. This result is supported by the low abundance of freshwater fish in the assemblages. However, it should be noted that the exclusion of reptiles from the analysis of habitat fidelity may distort the picture. Indeed, iguanas spend most of their time in trees found near permanent sources of water, whereas turtles can be found in a variety of freshwater habitats. The very large quantities of invertebrate remains recovered in the 1995 and 1996 excavations also provide evidence for the exploitation of freshwater habitats (Stanchly 1999). Unfortunately, the dietary importance of the identified species, namely the jute snails, apple snails, and pearly mussels, remains poorly understood (Powis 2004; Solis 2011). In sum, the combined presence of fish, iguanas, and turtles in the assemblages suggests that the Pacbitun Maya exploited riverine resources, perhaps in proportions slightly higher than that suggested by the habitat fidelity analysis. There is also evidence at Pacbitun for the procurement of resources from non-local habitats. The identification of marine fish, such as the parrotfish and grouper, is indicative 142 of long-distance trade or the exploitation of the Caribbean coast, located 150 km east from Pacbitun. Overall, animal procurement strategies during the Middle Preclassic seem to have focused on the exploitation of local terrestrial habitats, with possible access to resources acquired from distant locales, such as the Caribbean Sea. Foraging strategies appear to have targeted prey types that could be acquired at little distance from the site, particularly in secondary growth forests or agricultural fields. Patterns of habitat use are similar for both the early and late Middle Preclassic periods (K-S D = 0.2, p = 0.999). 7.7 Transport selectivity At Pacbitun, none of the species identified in the Middle Preclassic assemblages are represented by complete skeletons. As explained in Chapter 4, central place foragers who hunt large prey items often need to make decisions regarding which parts to bring home and which ones to leave behind. In order to investigate such decisions, archaeozoologists have developed indices of economic utility (e.g., Binford 1978; Metcalfe and Jones 1988; Morin 2007; Morin and Ready 2013). These indices assume that different skeletal parts yield different amounts of meat, marrow, and grease. As a result, skeletal elements can be ranked according to their food value. If foragers were highly selective about which parts to transport to a central place, skeletal elements of higher food utility should be more abundant in the archaeological record than those of low utility. However, if carcasses were brought whole, all skeletal elements should be present in roughly equal proportions. This observation may apply to three high-ranked species exploited at Pacbitun: white-tailed deer, red brocket deer, and peccary. Given that these large prey items all weigh less than 50 kg, it may have been 143 possible for a small group of foragers or even a single hunter to transport entire carcasses back to the site. The abundance of skeletal parts in the Pacbitun assemblages is compared here to different utility indices to determine if different currencies (e.g., meat, marrow, bone grease, raw material) guided transport decisions at Pacbitun. In Chapter 6, it was argued that bone portions of low density were underrepresented in the assemblages because of the effects of density-mediated processes, including differential preservation and carnivore ravaging. As a result, only elements of high bone density were selected for comparison with utility indices. According to the shape-adjusted reindeer bone density values provided by Lam and colleagues (1999), high-density portions for cervids are crania, mandibles, limb bone shafts, and the glenoid portion of the scapula. Although meat and marrow utility indices have been derived for white-tailed deer (Madrigal 2004), they were not used in this study because values were not available for all the elements which are of interest in this analysis. Three utility indices constructed for reindeer (Rangifer tarandus) were used instead (Binford 1978; Metcalfe and Jones 1988; Morin 2007). Because the anatomical structure of ungulates is similar across species (Lam et al. 1999), using indices constructed for another cervid should provide comparable results. The first utility index, named the simplified Meat Utility Index (MUI), measures the quantity of meat, marrow, and bone grease—or overall food content—of different skeletal parts (Metcalfe and Jones 1988). The simplified MUI is an intuitive measure of utility for the Pacbitun assemblages, because the residents of the site most likely consumed meat, as indicated by the presence of cutmarks, and extracted marrow from long bones (see section 7.8). The second utility measure can be termed the “grease index.” The data used to construct this index comes from an ethnographic episode 144 documented by Binford in spring 1971, during which he observed a Nunamiut woman selecting reindeer parts for bone grease rendering (Binford 1978). Data for phalanges in the MUI and grease index were obtained from Morin and Ready (2013), who corrected the values provided by Binford (1978) and Metcalfe and Jones (1988) to account for the fact that each foot in artiodactyls has two sets of three phalanges. The third economic measure is the Unsaturated Marrow Index (UMI) developed by Morin (2007). This index calculates the total quantity of unsaturated fatty acids in marrow-bearing bones, which are a major source of fats in ungulates. Figure 7.2 compares the NNISP values for a restricted set of white-tailed deer elements to the reindeer MUI, grease index, and UMI. Because of small sample size, the early and late Middle Preclassic assemblages were combined in the analysis (Table 7.1). It is expected that, if overall food value was the most important currency in transport decisions, the highest correlation should be found with the MUI. Instead, if within-bone fat content was the main currency in skeletal transport decisions, white-tailed deer skeletal abundances should correlate more strongly with the UMI or grease index. All three correlations with the utility indices are weak and non-significant (Table 7.6). This result suggests that the Pacbitun Maya were relatively non-selective in terms of which long bones were transported to the site. This result may not be surprising. Given the small size of white-tailed deer in the tropics, carcasses of this animal could have been transported whole to the site by a small foraging party. 145 120 100 MAN HUM MAX %NNISP 80 MC 60 FEM TIB 40 MT RAD 20 SCA 0 0 20 40 60 80 100 120 %MUI 120 100 %NNISP HUM 80 MC 60 FEM TIB 40 MT RAD 20 SCA 0 0 20 40 60 80 100 120 %grease 120 100 %NNISP HUM 80 MC 60 FEM TIB 40 RAD MT 20 0 0 20 40 60 80 100 120 %UMI Figure 7.2 Comparison of white-tailed deer element frequencies (%NNISP) in the Pacbitun assemblages with the reindeer MUI, grease index, and UMI. 146 Table 7.6 Spearman’s rank order correlations between skeletal part representation and the MUI, grease index, and UMI. n indicates the number of skeletal elements considered in the correlations. Index MUI Grease rendering UMI n 9 7 6 rs 0.08 0.45 –0.61 p 0.85 0.31 0.20 Before accepting this interpretation of transport decisions at Pacbitun, it may be necessary to review factors that may confound the results. The absence of correlation may result from small sample size. Indeed, the sample of white-tailed deer elements selected for analysis has a NISP of 46, which is very small. Additionally, because only a small number of categories of elements were considered (MUI n = 9; grease index n = 7; UMI n = 6), the statistical power of the comparisons is fairly low. An examination of the representation of other skeletal parts in the assemblages can provide further insight into transport decisions. As mentioned in section 7.2, crania and mandibles are the most common elements in the assemblages, although they are only represented by teeth. Because teeth are more easily identified than bone fragments, their representation may be inflated in the samples. Generally, it is considered that ungulate skulls are bulky, heavy, and of low nutritional value (Binford 1978). Ethnographic observations often report that skulls are discarded at kill sites because foragers do not want to invest energy in transporting skeletal elements which are considered of low profitability. However, as previously mentioned, this observation may not apply to small ungulates such as white-tailed deer which could be transported whole. At Pacbitun, the abundance of cranial and mandibular teeth suggests that these elements were frequently transported to the site. 147 Feet are another bulky skeletal portion which may not be brought back to a central place because of its marginal utility value (Binford 1978). At Pacbitun, the first and second phalanges of white-tailed deer are quite abundant (phalanx 1: n= 9, %NNISP = 25.0; phalanx 2: n = 8, %NNISP = 22.2), whereas the third phalanx is only represented by three specimens (%NNISP = 8.3%). Five sesamoids are also present. This high frequency of feet elements (16.9%) may suggest that they were not frequently discarded at kill sites. High abundances of these elements were also observed in the skeletal profiles of peccary (46.2%) and red brocket deer (29.4%). In sum, the absence of correlation between utility indices and long bone portions of high density suggests that the Pacbitun Maya regularly transported whole carcasses back to the site. The abundance of crania, mandibles, and feet elements in the Middle Preclassic assemblages seems to support this interpretation. 7.8 Processing of skeletal parts Given that the Pacbitun Maya were not selective regarding which skeletal elements should be transported back to the site, it may be possible to gain further insight into the decisions related to animal resource procurement by considering patterns of onsite skeletal part processing. At Pacbitun, long bones of white-tailed deer seem to have been systematically marrow-cracked. Green-bone fractures, which exhibit a curved fracture edge and a smooth fracture surface, were observed in high proportions (76.1%). This type of fracture can be produced during marrow cracking, although trampling and carnivore ravaging may also create this type of damage. Although the sample is small, the presence of green-bone fractures on the long bones of smaller artiodactyls (peccary and brocket deer) suggests that these species were subjected to marrow exploitation as well. 148 None of the notches in the Pacbitun assemblages were observed in association with gnaw marks or cutmarks. Although there is evidence for carnivore overprinting in the Pacbitun samples (Chapter 6), these animals only form a small fraction (3.8%) of the Middle Preclassic assemblages. As a result, most notches are believed to have been produced by anthropogenic fracturing. It should be noted that heavy weathering of the material made it difficult to observe notches on fracture edges. Frequent abrasion of the edges may have obscured the identification of notches. Intensity of marrow exploitation can be investigated through the examination of elements containing marginal amounts of marrow, such as the mandible, phalanges, calcaneum, and astragalus. In periods of food scarcity, humans may resort to extract marrow from some of these parts (Binford 1978). At Pacbitun, only white-tailed deer elements were considered in this analysis. In the early Middle Preclassic assemblage, all specimens of astragalus (n = 2), calcaneus (n = 3), first (n = 2) and second (n = 1) phalanges are fragmented, with the exception of two first phalanges which are complete. None of these elements bear traces of carnivore gnawing. The picture is similar for the late Middle Preclassic sample. Most elements with a small marrow cavity are fragmentary (calcaneus = 3/3; astragalus = 2/3; first phalanx = 5/5; second phalanx = 4/7). Although several specimens of calcaneum and first phalanges show edges consistent with green bone fractures, three specimens also display gnaw marks. As a result, it is difficult to determine whether phalanges and tarsals were fragmented as a result of marrow-cracking activities, carnivore ravaging, or both. Bone grease rendering may be another indicator of nutritional stress. Indeed, the extraction of bone grease is a strenuous activity with high processing costs and low returns (Brink 1997). Grease rendering is the most destructive of all butchering processes 149 and can result in extensive fragmentation of long bone epiphyses. If this activity had been systematically practiced at Pacbitun, epiphyses would be severely depleted in comparison with long bone shafts. Although epiphyses of white-tailed deer are less common than shafts, differences in frequency (shafts = 53.2%; proximal = 27.4%; distal = 19.4%) between the bone portions are not sharp (K-S D = 0.29, p = 0.88). Morin (2012:210) suggests that pounding and crushing marks associated with significant fragmentation of spongy bones may provide additional evidence for grease extraction. However, such marks were not observed in the Pacbitun samples. The destruction of epiphyses in the Pacbitun assemblages more likely results from carnivore ravaging and post-depositional destruction (Chapter 6). Burning of spongy bone may also create a similar signature in the archaeological record (Morin 2010), but there is little evidence for the use of bone as fuel at Pacbitun given that none of the burned specimens (n = 38) are from cancellous bone. Overall, marrow-cracking of long bones appear to have been systematic at the site. It is not possible to ascertain if marginal marrow-bearing elements were also exploited due to a lack of data. There is also little evidence for grease rendering during the Middle Preclassic at Pacbitun. 7.9 Pacbitun foraging strategies: A discussion At Pacbitun, it appears that the Middle Preclassic Maya concentrated their efforts on some of the most profitable prey items, such as white-tailed deer and other smaller artiodactyls. However, less profitable prey types were also occasionally included in the diet breadth. These resources consist of a wide variety of small- and medium-sized game (e.g., paca, agouti, opossum, rabbit, armadillo, iguana, and bird). It was suggested that felines and snakes were likely exploited by the Middle Preclassic Maya of Pacbitun. 150 However, it is not possible to determine whether they were procured for food, as a source of raw material, and/or as a result of symbolic importance. Although there is evidence for the acquisition of exotic resources, such as marine fish, these resources seem to have been very marginal to the diet. Domestic dogs do not appear to have been an important source of food. Vertebrate aquatic resources were also exploited, but in much smaller proportions than terrestrial animals. However, data presented by Stanchly (1999) regarding the exploitation of freshwater molluscs at Pacbitun tends to emphasize the importance of freshwater resources in the Maya diet. Freshwater molluscs represent 42.1% of the samples collected in 1995 and 1996. However, the importance of these animals may be over-estimated in this sample. First, molluscs are more easily identified than vertebrate remains. Second, as a result of their calcium carbonate composition, shell remains tend to preserve better than bone in highly acidic soil conditions. Third, although Stanchly argues that freshwater molluscs, particularly the jute, contributed significantly to the Preclassic diet, other authors (e.g., Solis 2011) disagree and conclude that their inclusion in the archaeological record may be incidental. For instance, 85.2% of the jute found during the 1995 and 1996 excavations were recovered from the thick secondary midden deposit which was laid on top of the Plaza B sub-structures at the end of the late Middle Preclassic period. It is possible that the jute were included in the midden as part of riverbed soils which would have been used to level the plaza floor. Overall, these data suggest that freshwater resources were infrequently acquired at Pacbitun. Because they are slow-moving animals which can be easily captured, turtles probably constituted an exception to this pattern. 151 Cannon (2003) explains that, when high-ranked resources are depleted from an environment, foragers need to invest more time in pursuing and acquiring lower-ranked prey types in order to continue maximizing their net delivery rate. This seems to have been the case at Pacbitun. Indeed, the scarcity of tapirs, the highest-ranked prey type, in the Pacbitun assemblages suggests that this prey item was infrequently encountered, possibly as a result of resource depression. Although the Pacbitun Maya are believed to be among the first settlers of the southern rim of the Belize River Valley, animal populations may have been under hunting pressure during earlier time periods, such as the Early Preclassic (2000–1000 BC) or even the Archaic period. The Pacbitun Maya seem to have responded to this situation by concentrating their foraging efforts on a relatively narrow set of smaller-sized, but still highly profitable, prey items. In sum, white-tailed deer, a relatively high-ranked species, appear to have formed the bulk of the diet at Pacbitun. Lower-ranked artiodactyls were also included in the diet, whereas a variety of other items may have been taken on occasion. The high frequency of long bones of white-tailed deer in the assemblages, combined with the abundance of crania, mandibles, tarsals, and phalanges, points to the frequent transport of whole carcasses. Animals were presumably exploited for their meat and marrow. Foraging clearly focused on the exploitation of terrestrial habitats, particularly those located near the site, with occasional trips taken to distant locales, such as mature forests and water sources. Although the early and late Middle Preclassic samples sometimes needed to be combined, the patterns of both assemblages seem consistent in terms of diet breadth, habitat use, and skeletal element exploitation. 152 7.10 Subsistence strategies in the southern Maya lowlands As mentioned earlier, research on the subsistence of the Maya during the Middle Preclassic period is very limited. Only a handful of faunal assemblages recovered in the southern lowlands and dating to this time period have been analyzed (Table 2.2). Unfortunately, some of these assemblages are affected by small sample size (e.g., Altar de Sacrificios, Seibal), which considerably limits interpretation of past subsistence strategies. Another prevalent problem is the lack of taphonomic data, as information on recovery methods and taphonomic history is not always available. Moreover, although evidence for anthropic manipulation is often mentioned, other factors that may cause differential preservation of faunal remains, including carnivore ravaging, weathering, and other density-mediated processes, are not reported. Keeping in mind these issues, one site from each of the sub-regions defined in Chapter 2 (i.e., Petén region of Guatemala, Belize River Valley, and northern Belize) was selected for comparison with the Pacbitun assemblages. It should be noted that questions regarding the exploitation of meat, marrow, or fat from skeletal elements of large mammals could not be explored because this issue is rarely addressed by the studies. The site of Cahal Pech is the only Middle Preclassic site from the Belize River Valley for which we have faunal data. Cahal Pech is located on the banks of the Belize River (Figure 2.1) and was occupied as early as the end of the Early Preclassic period (1200–900 BC). The faunal dataset presented in this analysis was recovered exclusively from the Tolok group, a small community established in the periphery of the site core (Powis et al. 1999). All faunal remains were found in an undisturbed midden deposit dated to the latter phase of the late Middle Preclassic period (450–300 BC). 153 The Cahal Pech assemblage is dominated by fish remains (95.4%, Table 7.7), the majority of which have not been identified beyond class level (Powis et al. 1999). This pattern is not surprising given that Cahal Pech is located at the junction of three major river systems, the Macal, Mopan, and Belize Rivers. Marine fish (0.9%) have also been identified. Their presence at an inland site located some 110 km away from the Caribbean coast is attributed either to the existence of long-distance trade networks or to direct exploitation of the coast by the Cahal Pech Maya. Interestingly, the presence of skull elements from marine fish, some of which present traces of burning, suggests that marine resources were transported whole to the site where they would have been processed and consumed (Powis et al. 1999). Terrestrial mammals are the second most important taxonomic group in the sample (2.0%), but they are only represented by eight taxa, including white-tailed deer, brocket deer, domestic dog, paca, armadillo, rabbit, opossum, and small rodents. White-tailed deer is the most common mammal at Cahal Pech (0.7% of total NISP), whereas other artiodactyls are rare (<0.1%). Powis and colleagues (1999) suggest that most of these species were acquired within the local environment. They conclude that the foraging strategies at Cahal Pech would have focused on the procurement of terrestrial herbivores, marine reef fish, and small quantities of freshwater fish. It should be noted that preliminary analyses of faunal assemblages recovered from Structure B-4 at Cahal Pech suggests that the residents of the site core focused on the exploitation of terrestrial mammals (57.7%) (Stanchly and Dale 1992). Fish was rarely identified in these last assemblages (6.5%). One wonders whether this disparity in taxonomic composition results from variations in recovery procedures, differential preservation, spatial distribution of faunal remains, or foraging strategies. 154 Table 7.7 Percentages of vertebrate taxa identified in Middle Preclassic assemblages at Pacbitun (this study), Tolok group at Cahal Pech (Powis et al. 1999), Colha (Shaw 1999) and Bayak (Emery 2010). Scientific Name Osteichthyes Siluriformes Serranidae Cichlidae Lepisoteiformes Sparisoma spp. Lachnolaimus spp. Lutjanidae Unidentified fish Amphibia Rhinella marina Reptilia Iguanidae Testudines Dermatemys sp. Emydidae Trachemys scripta Rhinoclemmys areolata Staurotypus sp. Chelydra serpentina Kinosternon spp. Colubridae Viperidae Crocodylidae Unidentified reptile Aves Galliformes Unidentified bird Mammalia Didelphis spp. Dasypus novemcinctus Canidae Canis lupus familiaris Nasua narica Mustela frenata Felidae Tapirus bairdii Artiodactyla Tayassuidae Cervidae Odocoileus virginianus Mazama americana Rodentia Orthogeomys spp. Dasyproctidae Cuniculus paca Dasyprocta punctata Sylvilagus spp. Total Common Name Catfish Grouper Cichlid Gar Parrotfish Hogfish Snappers Marine toad Iguana Turtle Central American River turtle Pond turtles Terrapin Furrowed wood turtle Musk turtles Common snapping turtle Mud turtle Colubrid Viper Crocodile Turkey, curassow Common opossum Nine-banded armadillo Dog, fox Domestic dog White-nosed coati Long-tailed weasel Cats Tapir Artiodactyl Peccary Cervid White-tailed deer Red brocket deer Pocket gopher Agoutis, pacas Paca, gibnut Agouti Rabbit Pacbitun Cahal Pech n = 292 n = 2171 95.4 2.7 0.3 0.1 0.3 <0.1 0.3 1.7 0.3 0.3 10.6 1.7 5.5 0.7 <0.1 <0.1 94.4 0.0 0.8 0.1 0.1 Colha n = 1550 40.8 Bayak n = 268 38.9 2.3 0.8 5.3 40.8 0.0 30.5 0.0 47.5 53.1 17.5 0.8 10.3 4.1 0.3 32.4 5.0 0.4 11.7 0.3 0.5 0.3 2.1 1.0 6.1 3.1 6.1 0.4 1.7 0.3 1.4 84.6 1.4 12.0 0.3 0.7 0.3 0.3 2.1 0.3 0.7 4.5 2.4 47.6 5.8 2.4 0.3 1.0 1.0 1.4 100.0 0.6 1.7 0.1 1.6 2.0 0.4 0.1 0.1 1.7 0.4 0.4 11.2 0.5 0.7 0.8 2.2 0.8 0.8 7.3 0.1 0.7 <0.1 0.2 0.1 1.7 4.4 0.1 0.4 0.4 5.0 0.8 0.3 0.1 0.4 0.3 0.1 100.0 0.2 0.1 100.0 0.4 100.0 155 A group of three sites in northern Belize, Colha, Cuello, and K’axob, was presented in Chapter 2 (Table 2.2). Because taxonomic composition is similar at the three sites (Kruskall-Wallis ANOVA4 H = 3.71, p = 0.155), only one site is presented here. Colha is located in northern Belize, roughly 45 km from the Caribbean Coast, near Rancho Creek (Shaw 1999). The faunal assemblages discussed here were recovered from middens associated with domestic structures (Operations 2012 and 2031). During the Middle Preclassic, the Colha Maya appear to have taken advantage of local terrestrial and aquatic habitats and strongly focused on the exploitation of wetlands. This is evidenced by the predominance of fish (40.8%) and turtles (45.2%) in the samples (Table 7.7). Unfortunately, although both freshwater and marine fish were identified, the majority of fish remains could rarely be identified beyond class level. According to Shaw (1999), the small size of the fish vertebrae is more consistent with the anatomy of freshwater than marine fish. Therefore, she believes that most fish in the samples are from freshwater habitats. A fuller analysis of the fish remains will be needed to resolve this issue. A variety of terrestrial mammals (n = 11) were also exploited and form a small portion of the assemblages (11.2%). White-tailed deer (4.4%) and the domestic dog (2.2%) are the most common mammals. From the three sites in the Petén region of Guatemala, only Bayak (Emery 1997) had a sample size sufficient for comparisons with other sites. Indeed, the identified vertebrate assemblages from Altar de Sacrificios (n = 24) and Seibal (n = 72) are very small. Bayak is a very small Preclassic site located on the edge of the Petexbatun Lake, in Guatemala. Fish (38.9%) and turtles (52.7%) form the bulk of the samples, whereas 4 The Kruskall-Wallis ANOVA test was preferred over the chi-square test of independence because the assumptions of the latter test were not met by the datasets compared in this analysis. 156 terrestrial mammals, dominated by white-tailed deer (5.0%), only constitute a small part of the assemblage (7.3%). Fish are represented by almost equal proportions of cranial and axial elements, suggesting that they were used whole or prepared at the site. Analysis of habitat fidelity for the site of Bayak shows that riverine (75.5%) and swamp (21.8%) habitats were frequently used by the residents of the site (Emery 1997). These results are consistent with the location of the site on an elevated shoreline of the Petexbatun River. Non-local faunal remain, such as marine fish, were not identified at this inland site. Overall, data from Pacbitun, Colha, Cahal Pech, and Bayak suggest that the Middle Preclassic Maya adopted foraging strategies consistent with the habitats in which they lived. Regional variation in species use is relatively high. In fact, differences in taxonomic composition between the four faunal assemblages are statistically significant (Kruskal-Wallis ANOVA H = 16.8, p = 0.0008) (Table 7.8). Kolmogorov-Smirnov tests show that differences are not statistically significant for two pairs of sites: Cahal Pech and Colha, and Cahal Pech and Bayak, possibly as a result of similar strategies of animal procurement. Indeed, faunal analyses show that the residents of these sites largely subsisted on fish and did not exploit terrestrial mammals in large quantities. Table 7.8 Results of the Kolmogorov-Smirnov tests for the Middle Preclassic assemblages from the southern lowlands. Sites Pacbitun Cahal Pech Colha Bayak Pacbitun – 0.75 0.60 0.67 Cahal Pech <0.001 – 0.33 0.44 Colha <0.001 0.31 – 0.55 Bayak <0.001 0.14 0.002 – Values below the dashes correspond to the D value, while those above are the p-values. During the Middle Preclassic, the emphasis appears to have been placed on the exploitation of resources available in local micro-environments. Pacbitun, a site 157 surrounded by the tropical forest, is the only one where the population apparently focused on the exploitation of terrestrial animals of intermediate and large size. Conversely, the Maya of Colha, which cultivated both milpas and wetlands, took advantage of the resources they could acquire in the vicinity of agricultural fields. This includes turtles, freshwater fish and, to a lesser extent, terrestrial mammals. The residents of Bayak, which lived on the shore of a large lake, focused nearly exclusively on the exploitation of freshwater fish and turtles. Cahal Pech is the only site which presented variation in the taxonomic composition of the assemblages recovered at the site. At Tolok, fish clearly dominate the sample, whereas preliminary analyses of samples recovered from the site core (Structure B-4) indicate that terrestrial mammals were the most common resources acquired in this part of the site. Because of a lack of data on the taphonomic history of these assemblages and the preliminary nature of the faunal analysis of Structure B-4, it is not possible to identify the cause(s) of this variation. The presence of marine fish at some of these sites is also surprising. Table 7.9 presents the frequencies of marine fish at southern lowlands sites, with the average distance between each site and the Caribbean coast. As expected, no specimens of marine fish were recovered at the sites located in the Petén region of Guatemala, at a distance of 250–400 km from the coast. However, it is surprising that remains of marine fish were not identified at the two sites located closest to the Caribbean Sea, that is, K’axob and Colha. It is suggested that this absence may result from an incomplete analysis of the fish samples. Indeed, significant quantities of fish remains were recovered from both sites, but a majority of specimens were not identified beyond class level. This explanation remains speculative. Small quantities of marine fish were also identified at Cuello, a site located about 35–50 km from the coast. 158 Table 7.9 Abundances of marine fish at southern lowlands Maya sites during the Middle Preclassic period, with average distances from the coast of the Caribbean Sea. Sites K'axob Colha Cuello Cahal Pech Pacbitun Bayak Seibal Altar de Sacrificios NISP 0 0 30 28 2 0 0 0 % 0 0 0.49 1.18 0.68 0 0 0 Distance 15–20 km 20 km 35–50 km 110 km 150 km 250–300 km 300 km 400 km Sources: Altar de Sacrificios (Pohl 1990), Bayak (Emery 2010), Cahal Pech (Stanchly 1995; Powis et al. 1999), Cuello (Wing and Scudder 1991; Carr and Fradkin 2008), Colha (Shaw 1999), K’axob (Masson 2004a), Pacbitun (this study), and Seibal (Pohl 1990). The most surprising finds come from the inland sites of Cahal Pech and Pacbitun, where remains of parrotfish, grouper, and snapper were identified. Stable isotope analysis of carbon and nitrogen at Cahal Pech suggests that reef fish were consumed on a regular basis. This result appears incompatible with the location of the site, as well as with the very small amounts of marine fish in the archaeological assemblages (1.2%). It is suggested that differential preservation, sampling strategy, and/or difficulty of distinguishing between freshwater and marine fish species may explain the scarcity of marine fish at Cahal Pech, but also at other southern lowland sites. Overall, marine fish only formed a very small portion of the assemblages at the sites where they have been identified. No correlation was found between the quantity of fish identified in the faunal assemblages and a site’s distance from the Caribbean Sea (rs = –0.13, p = 0.74). Additionally, it was not also possible to determine whether the presence of marine fish at Middle Preclassic sites reflect long-distance fishing trips or the beginnings of exchange of goods between communities located in different habitats. 159 A point should be made concerning the argument that domestic dogs were heavily used as a source of food during the Preclassic period. This pattern, which was first inferred at Cuello (Clutton-Brock and Hammond 1994), is not supported at Pacbitun, Bayak, or Cahal Pech. However, Shaw (1991) reported that there is unambiguous evidence for the consumption of dogs at Colha in the form of cutmarks. She also explains that many bones are burned, a situation which she attributes to the cooking of these animals for food consumption. It is suggested here that the use of dogs as a source of food during the Middle Preclassic period may have been a restricted to northern Belize. Lastly, the taxonomic composition from Colha, Cahal Pech, and Bayak suggests that, contrary to what was found at Pacbitun, the prey items most frequently taken were not always be the largest in terms of body mass. In fact, terrestrial mammals only form a small portion of the assemblages, with ungulates generally constituting the most abundant terrestrial taxa (Cahal Pech = 0.7% of NISP; Colha = 6.3%; Bayak = 6.5%). According to the central place forager prey choice model, the scarcity of large terrestrial game may indicate depletion of these resources in patches located near the three sites. In fact, the emphasis placed on the exploitation of other less profitable resources at Cahal Pech, Bayak, and Colha may reflect a broadening of the diet. Fish, an important resource at the three sites, was perhaps favored because it can be mass-collected with the use of nets. This fishing technology can increase the net return rate of energy acquisition, particularly if small fish do not need to be processed extensively. The exploitation of turtles also seems to have been the focus of foraging strategies at Bayak and Colha, two sites which had access to many water sources. As previously mentioned, turtles are slow-moving animals which can provide important quantities of meat for little costs. As such, they may always have been part of the optimal diet. 160 CHAPTER 8: CONCLUSION This study has investigated the foraging strategies related to the acquisition of animal resources during the Middle Preclassic period at the ancient Maya site of Pacbitun. This concluding chapter revisits the objectives outlined in Chapter 1 and summarizes the findings of the faunal analysis. It also examines several limitations of this study and considers the significance of this research. Recommendations for future research are also provided. 8.1 Research summary The results of this study are summarized here according to the objectives outlined in Chapter 1. 1) Taphonomic analysis: A detailed analysis of the Pacbitun faunal assemblages has revealed that several taphonomic processes have shaped the samples. The use of two different recovery methods does not seem to have affected the taxonomic composition of the assemblages, although selective recovery may have depleted the assemblages of specimens smaller than 1 cm. A majority of faunal remains have been severely affected by weathering, a situation which impeded taxonomic identification and possibly obliterated the identification of marks left on bone surfaces. Carnivores, in particular domestic dogs, appear to have had secondary access to the bone deposits and possibly altered the assemblages. Depletion of elements and bone portions of low density may also result from post-depositional destruction and perhaps burning. Findings of the taphonomic analysis were similar for both the early and late Middle Preclassic assemblages, although bones surfaces were more poorly preserved in the late Middle Preclassic sample. 161 2) Analysis of foraging strategies at Pacbitun: Archaeozoological analysis of the faunal samples indicates that the Middle Preclassic Maya of Pacbitun exploited a wide variety of vertebrate animal resources, including mammals, reptiles, fish, and birds. Animal procurement strategies focused on the exploitation of ungulate species, with white-tailed deer constituting by far the primary prey item. The most profitable prey types according to the body mass scale, that is, the tapir, jaguar, and puma, seem to have been infrequently encountered. Low-ranked prey taxa were occasionally exploited. These included a variety of small- and medium-sized game. Secondary growth forests and agricultural fields, two habitat types which would have been located at short distance from the site, were the primary focus of hunting activity. The low abundances of freshwater resources and forest-dwelling animals suggest that riverine areas and mature forests were less heavily utilized. Analysis of skeletal patterns suggests that the carcasses of large ungulates were transported whole to the site. Animal resources appear to have been exploited for their meat and marrow fat content. Labor-intensive activities, such as bone grease rendering and marrow-cracking of marginal marrow-bearing elements, do not appear to have been practiced on a regular basis. 3) Animal resource exploitation in the southern Maya lowlands: Comparisons of faunal assemblages from four Maya sites suggest that, during the Middle Preclassic, procurement of animal resources focused on taxa which could be acquired in local habitats. Exotic resources, such as marine fish, were also imported in small quantities to sites located inland. This possibly attests to the presence of longdistance trade networks during this early time period. The foraging patterns identified at 162 Pacbitun differ from those observed at Cahal Pech, Colha, or Bayak. People at these three sites relied more heavily on fish and, in the case of Colha and Bayak, turtles. While large terrestrial game is the prey item most frequently taken at Pacbitun, it only forms a fraction of the assemblages at other Middle Preclassic sites. It is suggested that depletion of largesized prey types in patches located near the sites may have led to a broadening of the diet and the subsequent exploitation of less profitable resources, such as fish. 8.2 Limitations and significance The primary limiting factor of this investigation is the small sample size of the Pacbitun assemblages (early Middle Preclassic NISP = 125; late Middle Preclassic NISP = 167). In some instances, this situation precluded comparisons of the early and late Middle Preclassic samples. Additionally, because of small sample size, many species were only represented by one or two specimens. In those cases, the question remains of whether these taxa are rare in the assemblages as a result of sample size or because they were not exploited by the ancient Maya. Additionally, as a result of small sample size, the statistical power of this study is fairly low. Indeed, in order for statistical tests to be robust (i.e., to identify significant relationships among data), samples must be relatively large. This is because the effect of outliers is much greater in small samples, a situation which can obscure or exaggerate trends within the sample. To control for this situation, nonparametric statistical tests were employed in this study because they are less prone to the effects of small sample sizes and abnormally distributed data than parametric tests (Chenorkian 1996). Despite small sample size, trends emerged from the analysis of the Pacbitun faunal data, such as a clear focus on the exploitation of white-tailed deer by the residents of the site. Hopefully, 163 continuing research at Pacbitun should help to increase the size of the faunal samples and confirm the patterns observed in this study. Despite these limitations, this study shows that the Pacbitun Maya took advantage of resources locally available, focusing mainly on large prey items such as artiodactyls. The data also lend support to the notion that foraging strategies during the Middle Preclassic were highly focused on the exploitation of local habitats. Although there is evidence for the acquisition of animal resources from distant locales, the vast majority of prey items were acquired in the vicinity of the sites. 8.3 Future Directions Although it was shown in this study that the use of different screen mesh sizes did not affect the Pacbitun assemblages in terms of fragment size or taxonomic composition, it is suggested that finer mesh screens should be used in the future in order to increase the chances of recovering smaller specimens and/or taxa. However, the use of finer mesh screens is a relatively time-consuming activity, particularly when soils are of clay composition as it is the case at Pacbitun. A reasonable strategy might be to draw random soil samples and to screen them with fine mesh screens (e.g., 1/8 or 1/16 inch mesh screen) to determine which mesh size is the most adequate for maximizing the recovery of faunal remains. It is should be noted that the use of finer mesh screens do not necessarily lead to the increased recovery of faunal remains because small remains may have disappeared in poorly preserved faunal assemblages. Because the Maya exploited animals for economic, social, political, and religions purposes, faunal data alone may not always be sufficient to detect the multiple ways in which animals were used. As a result, it is suggested that many lines of evidence should 164 be used to interpret faunal data. Alongside iconographic, ethnohistoric and ethnographic records which are typically used by Maya zooarchaeologists, evidence for past animal use may be obtained from more recently developed methods, such as residue analysis and stable isotope analysis. For instance, at Pacbitun, the analysis of habitat fidelity only provided coarse information about the provenience of the animals exploited by the site’s residents. However, given the location of Pacbitun between two ecozones, the tropical rainforest and the pine ridge, it may be interesting to determine if prey taxa were preferably acquired from one of these two ecozones or even if animals, in particular terrestrial species, might have been procured from the Belize River Valley or other regions in the southern lowlands. Had the scope of this research been larger, this question could have been investigated through strontium isotope analysis. 165 BIBLIOGRAPHY Álvarez, M. C., C. A. Kaufmann, A. Massigoge, M. A. Gutiérrez, D. J. Rafuse, N. A. Scheifler and M. E. González 2012 Bone Modification and Destruction Patterns of Leporid Carcasses by Geoffroy’s Cat (Leopardus geoffroyi): An Experimental Study. Quaternary International 278:71–80. Anderson, D. S. 2011 Xtobo, Yucatan, Mexico, and the Emergent Preclassic of the Northern Maya Lowlands. Ancient Mesoamerica 22:301–322. Andrews, E. W. I. 1969 The Archaeological Use and Distribution of Mollusca in the Maya Lowlands. Middle American Research Institute Publication 34. Tulane University, New Orleans. Andrews, E. W. I., M. P. Simmons, E. S. Wing, E. W. V. Andrews and J. M. Andrews (editors) 1974 Excavations of an Early Shell Midden on Isla Cancún, Quintana Roo, Mexico. Middle American Research Institute Publication 21. Tulane University, New Orleans. Andrews, P. and E. M. N. Evans 1983 Small Mammal Bone Accumulations Produced by Mammalian Carnivores. Paleobiology 9:289–307. Arendt, C., S. Rhan-Ju and P. F. Healy 1996 The 1995 Excavations in Plaza C, Pacbitun, Belize: A Middle Preclassic Burial and a Late Classic Stela. In Belize Valley Preclassic Maya Project: Report on the 1995 Field Season, edited by P. F. Healy and J. J. Awe, pp. 128–138. Occasional Papers in Anthropology 12. Trent University, Peterborough. Awe, J. J. 1992 Dawn in the Land Between the Two Rivers: Formative Occupation at Cahal Pech, Belize and Its Implications for Preclassic Occupation in the Central Maya Lowlands. Unpublished Ph.D. dissertation, Institute of Archaeology, University of London, London. Awe, J. J., P. F. Healy, C. M. Stevenson and B. Hohmann 1996 Preclassic Maya Obsidian in the Belize Valley. In Belize Valley Preclassic Maya Project: Report on the 1995 Field Season, edited by P. F. Healy and J. J. Awe, pp. 153–174. Occasional Papers in Anthropology 12. Trent University, Peterborough. 166 Ball, J. W. and J. T. Taschek 2004 Buenavista del Cayo: A Short Outline of Occupational and Cultural History at an Upper Belize Valley Regal-Ritual Center. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological Research, edited by J. F. Garber, pp. 149–167. University Press of Florida, Gainesville. Barone, R. 1986 Anatomie Comparée des Mammifères Domestiques : Tome 1 Ostéologie. 3rd ed. Vigot, Paris. Behrensmeyer, A. K. 1978 Taphonomic and Ecologic Information from Bone Weathering. Paleobiology 4:150–162. Behrensmeyer, A. K., C. T. Stayton and R. E. Chapman 2003 Taphonomy and Ecology of Modern Avifaunal Remains from Amboseli Park, Kenya. Paleobiology 29:52–70. Bill, C. 1987 Excavations of Structure 23: A Maya Palace at the Site of Pacbitun, Belize. Unpublished M.A. thesis, Department of Anthropology, Trent University, Peterborough. Binford, L. R. 1978 Nunamiut Ethnoarchaeology. Academic Press, London. 1981 Bones: Ancient Men and Modern Myths. Academic Press, London. 1984 Faunal Remains from River Klasies Mouth. Academic Press, New York. Bird, D. W. and R. Bliege Bird 1997 Contemporary Shellfish Gathering Strategies among the Meriam of the Torres Strait Islands, Australia: Testing Predictions of a Central Place Foraging Model. Journal of Archaeological Science 24:39–64. Bird, D. W., R. Bliege Bird and B. F. Codding 2009 In Pursuit of Mobile Prey: Martu Hunting Strategies and Archaeofaunal Interpretation. American Antiquity 74:3–29. Bird, D. W., B. F. Codding, R. Bliege Bird and D. W. Zeanah 2012 Risky Pursuits: Martu Hunting and the Effects of Prey Mobility: Reply to Ugan and Simms. American Antiquity 77:186–194. Bird, D. W. and J. F. O'Connell 2006 Behavioral Ecology and Archaeology. Journal of Archaeological Research 14:143–188. 167 Brink, J. W. 1997 Fat Content in Leg Bones of Bison bison, and Applications to Archaeology. Journal of Archaeological Science 24:259–274. Bronson, B. 1966 Roots and the Subsistence of the Ancient Maya. Southwestern Journal of Anthropology 22:251–279. Broughton, J. M. 1994 Declines in Mammalian Foraging Efficiency during the Late Holocene, San Francisco, California. Journal of Anthropological Archaeology 13:371–401. Broughton, J. M., M. D. Cannon, F. E. Bayham and D. A. Byers 2011 Prey Body Size and Ranking in Zooarchaeology: Theory, Empirical Evidence, and Applications from the Northern Great Basin. American Antiquity 76:403–428. Broughton, J. M., D. Mullins and T. Ekker 2007 Avian Resource Depression or Intertaxonomic Variation in Bone Density? A Test with San Francisco Bay Avifaunas. Journal of Archaeological Science 34:374–391. Brown, C. T. and W. R. T. Witschey 2008 The Electronic Atlas of Ancient Maya Sites. Electronic document, http://mayagis.smv.org/maps_of_the_maya_area.htm, accessed November 22, 2012. Brown, K. M. 2007 Ritual ceramic use in the Early and Middle Preclassic at the sites of Blackman Eddy and Cahal Pech, Belize. Report submitted to the Foundation for the Advancement of Mesoamerican Studies (FAMSI). Brown, L. and P. Sheets 2000 Distinguishing Domestic from Ceremonial Structures in Southern Mesoamerica: Suggestions from Cerén, El Salvador. MAYAB 13:11–21. Brown, L. A. 2005 Planting the Bones: Hunting Ceremonialism at Contemporary and Nineteenth-Century Shrines in the Guatemalan Highlands. American Antiquity 16:131–146. Brown, R. D. 1994 Digestion. In Deer, edited by D. Gerlach, S. Atwater and J. Schnell, pp. 66–70. Stackpole Books, Mechanicsburg. 168 Buikstra, J. E. and M. Swegle 1989 Bone Modification Due to Burning: Experimental Evidence. In Bone Modification, edited by R. Bonnichsen and M. H. Sorg, pp. 247–258. Peopling of the Americas Publications. Center for the Study of the First Americans, Institute of Quaternary Studies, University of Maine, Orono. Bunn, H. T. 1983a Comparative Analysis of Modern Bone Assemblages from a San HunterGatherer Camp in the Kalahari Desert, Botswana, and from a Spotted Hyena Den near Nairobi, Kenya. In Animals and Archaeology 1: Hunters and their Prey, edited by J. Clutton-Brock and C. Grigson, pp. 143–148. BAR International Series Vol. 163. British Archaeological Reports, Oxford. 1983b Evidence on the Diet and Subsistence Patterns of Plio-Pleistocene Hominids at Koobi Fora, Kenya, and Olduvai Gorge, Tanzania. In Animals and Archaeology 1: Hunters and their Prey, edited by J. Clutton-Brock and C. Grigson, pp. 21–30. BAR International Series Vol. 163. British Archaeological Reports, Oxford. 1989 Diagnosing Plio-Pleistocene Hominid Activity with Bone Fracture Evidence. In Bone Modification, edited by R. Bonnichsen and M. H. Sorg. Peopling of the Americas Publications. Center for the Study of the First Americans, Institute of Quaternary Studies, University of Maine, Orono. Bunn, H. T. and E. M. Kroll 1986 Systematic Butchery by Plio/Pleistocene Hominids at Olduvai Gorge, Tanzania. Current Anthropology 27:430–452. Butler, V. L. 1990 Distinguishing Natural from Cultural Salmonid Deposits in Pacific Northwest North America. Unpublished Ph.D. dissertation, Department of Anthropology, University of Washington, Seattle. 1993 Natural Versus Cultural Salmonid Remains: Origin of the Dalles Roadcut Bones, Columbia River, Oregon, U.S.A. Journal of Archaeological Science 20:1– 24. Butler, V. L. and J. C. Chatters 1994 The Role of Bone Density in Structuring Prehistoric Salmon Bone Assemblages. Journal of Archaeological Science 21:413–424. Butler, V. L. and R. A. Schroeder 1998 Do Digestive Processes Leave Diagnostic Traces on Fish Bones? Journal of Archaeological Science 25:957–971. 169 Campbell-Trithart, M. J. 1990 Ancient Maya Settlement at Pacbitun, Belize. Unpublished M.A. thesis, Department of Anthropology, Trent University, Peterborough. Campbell, J. A. 1998 Amphibians and Reptiles of Northern Guatemala, the Yucatán, and Belize. University of Oklahoma Press, Norman. Cannon, M. D. 2000 Large Mammal Relative Abundance in Pithouse and Pueblo Period Archaeofaunas from Southwestern New Mexico: Resource Depression among the Mimbres-Mogollon? Journal of Anthropological Archaeology 19:317–347. 2003 A Model of Central Place Forager Prey Choice and an Application to Faunal Remains from the Mimbres Valley, Mexico. Journal of Anthropological Archaeology 22:1–25. Capaldo, S. D. and R. J. Blumenschine 1994 A Quantitative Diagnosis of Notches Made by Hammerstone Percussion and Carnivore. American Antiquity 59:724–748. Carr, H. S. 1985 Subsistence and Ceremony: Faunal Utilization in a Late Preclassic Community at Cerros, Belize. In Prehistoric Lowland Maya Environment and Subsistence Economy, edited by M. D. Pohl, pp. 115–132. Papers of the Peabody Museum of Archaeology and Ethnology Vol. 77. Harvard University, Cambridge. 1986 Faunal Utilization in a Late Preclassic Maya Community at Cerros, Belize. Unpublished Ph.D. dissertation, Department of Anthropology, Tulane University, New Orleans. 1996 Precolombian Maya Exploitation and Management of Deer Populations. In The Managed Mosaic: Ancient Maya Agriculture and Resource Use, edited by S. L. Fedick, pp. 251–261. University of Utah Press, Salt Lake City. Carr, H. S. and A. Fradkin 2008 Animal Resource Use in Ecological and Economic Context at Formative Period Cuello, Belize. Quaternary International 191:144–153. Casteel, R. W. 1972 Some Biases in the Recovery of Archaeological Faunal Remains. Proceedings of the Prehistoric Society 38:382–388. Castel, J.-C. 2004 L'Influence des Canidés sur la Formation des Ensembles Archéologiques: Caractérisation des Destructions Dues au Loup. Revue de Paléobiologie 23(2):675–693. 170 Chapman, J. A., J. G. Hockman and M. M. Ojeda 1980 Sylvilagus floridanus. Mammalian Species 136:1–8. Charnov, E. L. 1976 Optimal Foraging, the Marginal Value Theorem. Theoretical Population Biology 9:129–136. Chase, A. F., D. Z. Chase and W. G. Teeter 2004 Archaeology, Faunal Analysis and Interpretation: Lessons from Maya Studies. Archaeofauna 13:11–18. Chase, A. F. and J. F. Garber 2004 The Archeology of the Belize Valley in Historical Perspective. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological Research, edited by J. F. Garber, pp. 1–14. University Press of Florida, Gainesville. Chenorkian, R. 1996 Pratique Archéologique Statistique et Graphique. Errance, Paris. Cheong, K. F. 2013 Archaeological Investigations of the North Group at Pacbitun, Belize: The Function, Status, and Chronology of an Ancient Maya Epicenter Residential Group. Unpublished M.A. thesis, Department of Anthropology, Trent University, Peterborough. Clark, J. L. and B. Ligouis 2010 Burned Bone in the Howieson's Poort and Post-Howieson's Poort Middle Stone Age Deposits at Sibudu (South Africa): Behavioral and Taphonomic Implications. Journal of Archaeological Science 37:2650–2661. Cliff, M. B. and C. J. Crane 1989 Changing Subsistence Economy at a Late Preclassic Maya Community. In Prehistoric Maya Economies of Beliz, edited by P. A. McAnany and B. L. Isaac, pp. 295–324. JAI Press, London. Clutton-Brock, J. and N. Hammond 1994 Hot Dogs: Comestible Canids in Preclassic Maya Culture at Cuello, Belize. Journal of Archaeological Science 21:819–826. Coe, W. R. 1959 Piedras Negras Archaeology: Artifacts, Caches, and Burials. University Museum Monograph 18. University Museum, University of Pennsylvania, Philadelphia. 171 Collins, L. M. 2002 The Zooarchaeology of the Copan Valley: Social Status and the Search for a Maya Slave Class. Unpublished Ph.D. dissertation, Department of Anthropology, Harvard University, Cambridge. Colunga-García Marín, P. and D. Zizumbo-Villarreal 2004 Domestication of Plants in Maya Lowlands. Economic Botany 58:S101– S110. Covich, A. P. 1983 Mollusca: A Contrast in Species Diversity from Aquatic and Terrestrial Habitats. In Pulltrouser Swamp: Ancient Maya Habitat, Agriculture, and Settlement in Northern Belize, edited by B. L. Turner II and P. D. Harrison, pp. 120–139. University of Texas Press, Austin. Coyston, S. L., C. D. White and H. P. Schwarcz 1999 Dietary Carbonate Analysis of Bone and Enamel for Two Sites in Belize. In Reconstructing Ancient Maya Diet, edited by C. D. White, pp. 221–243. University of Utah Press, Salt Lake City. Cruz-Uribe, K. 1991 Distinguishing Hyena from Hominid Bone Accumulations. Journal of Field Archaeology 18:467–486. Cruz, I. 2008 Avian and Mammalian Bone Taphonomy in Southern Continental Patagonia: A Comparative Approach. Quaternary International 180:30–37. Demarest, A. 2004 Ancient Maya: The Rise and Fall of a Rainforest Civilization. Cambridge University Press, Cambridge. Dirrigl, F. J. 2001 Bone Mineral Density of Wild Turkey (Meleagris gallopavo) Skeletal Elements and Its Effects on Differential Survivorship. Journal of Archaeological Science 18:467–486. Donkin, R. A. 1985 The Peccary – With Observations on the Introduction of Pigs to the New World. Transactions of the American Philosophical Society Vol. 75. American Philosophical Society, Philadelphia. Doyle, J. A. 2012 Regroups on "E-Groups": Monumentality and Early Centers in the Middle Preclassic Maya Lowlands. Latin American Antiquity 23:355–379. 172 Duffy, L. G. 2011 Maize and Stone: A Functional Analysis of the Manos and Metates of Santa Rita Corozal, Belize. Unpublished M.A. thesis, Department of Anthropology, University of Central Florida, Orlando. Elder, W. H. 1965 Primeval Deer Hunting Pressures Revealed by Remains from American Indian Middens. Journal of Wildlife Management 29:366–370. Emery, K. F. 1997 The Maya Collapse: A Zooarchaeological Investigation. Unpublished Ph.D. dissertation, Department of Anthropology, Cornell University, Ithaca. 1999 Continuity and Variability in Postclassic and Colonial Animal Use at Lamanai and Tipu, Belize. In Reconstructing Ancient Maya Diet, edited by C. D. White, pp. 63–82. University of Utah Press, Salt Lake City. 2003 The Noble Beast: Status and Differential Access to Animals in the Maya World. World Archaeology 34(3):498–515. 2004a In Search of Assemblage Comparability: Methods in Maya Zooarchaeology. In Maya Zooarchaeology: New Directions in Method and Theory, edited by K. F. Emery, pp. 15–33. Monograph 51. Cotsen Institute of Archaeology, University of California, Los Angeles. 2004b Making the Most of the Data: Issues of Method and Theory in Tropical Zooarchaeology. Archaeofauna 13:7–10. 2004c Maya Zooarchaeology: Historical Perspectives on Current Research Directions. In Maya Zooarchaeology: New Directions in Method and Theory, edited by K. F. Emery, pp. 1–11. Monograph 51. Cotsen Institute of Archaeology, University of California, Los Angeles. 2007a Aprovechamiento de la Fauna en Piedras Negras: Dieta, Ritual y Artesanía del Periodo Clásico Maya. MAYAB 19:51–69. 2007b Assessing the Impact of Ancient Maya Animal Use. Journal for Nature Conservation 15(3):184–195. 2008a Techniques of Ancient Maya Bone Working: Evidence from a Classic Maya Deposit. Latin American Antiquity 19:204–221. 2008b A Zooarchaeological Test for Dietary Resource Depression at the End of the Classic Period in the Petexbatun, Guatemala. Human Ecology 36:617–634. 173 2009 Perspectives on Ancient Maya Bone Crafting from a Classic Period BoneArtifact Manufacturing Assemblage. Journal of Anthropological Archaeology 28:458–470. 2010 Dietary, Environmental, and Societal Implications of Ancient Maya Animal Use in the Petexbatun: A Zooarchaeological Perspective on the Collapse. Vanderbilt Institute of Mesoamerican Archaeology Vol. 5. Vanderbilt University Press, Nashville. Emery, K. F. and L. A. Brown 2012 Maya Hunting Sustainability: Perspectives from Past and Present. In The Ethics of Anthropology and Amerindian Research: Reporting in Environmental Degradation and Warfare, edited by R. J. Chacon and R. G. Mendoza, pp. 79– 116. Springer, New York. Emery, K. F. and E. K. Thornton 2008a A Regional Perspective on Biotic Change during the Classic Maya Occupation using Zooarchaeological Isotopic Chemistry. Quaternary International 191:131–143. 2008b Zooarchaeological Habitat Analysis of Ancient Maya Landscape Changes. Journal of Ethnobiology 28:154–178. Emery, K. F., L. E. Wright and H. Schwarcz 2000 Isotopic Analysis of Ancient Deer Bone: Biotic Stability in Collapse Period Maya Land-Use. Journal of Archaeological Science 27:537–550. Emmons, L. H. 1997 Neotropical Rainforest Mammals: A Field Guide. 2nd ed. University of Chicago Press, Chicago. Enloe, J. G. and F. David 1989 Le Remontage des Os par Individus : Le Partage du Renne chez les Magdaléniens de Pincevent (La Grande Paroisse, Seine-et-Marne). Bulletin de la Société Préhistorique Française 86(9):275–281. 1992 Food Sharing in the Paleolithic: Carcass Refitting at Pincevent. In Piecing Together the Past: Applications of Refitting Studies in Archaeology, edited by J. L. Hofman and J. G. Enloe, pp. 296–315. BAR International Series 578. British Archaeological Reports, Oxford. Estrada-Belli, F. 2011 The First Maya Civilization: Ritual and Power before the Classic Period. Routledge, London and New York. 174 Fairnell, E. 2008 101 Ways to Skin a Fur-Bearing Animal: The Implications for Zooarchaeological Interpretation. In Experiencing Archaeology by Experiment: Proceedings of the Experimental Archaeology Conference, Exeter 2007, edited by P. Cunningham, J. Heeb and R. Paardekooper, pp. 47-60. Oxbow Books, Oxford. Feldman, L. 1978 Seibal and the Mollusks of the Usumacinta Valley. In Excavations at Seibal, edited by G. R. Willey, pp. 166–167. Memoirs of the Peabody Museum of Archaeology and Ethnology Vol. 14, No. 1–3. Harvard University, Cambridge. Fernández-Jalvo, Y., B. Sánchez-Chillón, P. Andrews, S. Fernández-Lopez and L. Alcalá Martínez 2002 Morphological Taphonomic Transformations of Fossil Bones in Continental Environments, and Repercussions on their Chemical Composition. Archaeometry 3:353–361. Ford, L. S. and R. S. Hoffmann 1988 Potos flavus. Mammalian Species 321:1–9. Fradkin, A. 2004 Snake Consumption among Early Inhabitants of the River of Grass, South Florida, USA. Archaeofauna 13:57–69. Fradkin, A. and H. S. Carr 2003 Middle Preclassic Landscapes and Aquatic Resource Use at Cuello, Belize. Bulletin of the Florida Museum of Natural History 44(1):35–42. Freiwald, C. R. 2010 Dietary Diversity in the Upper Belize River Valley: A Zooarchaeological and Isotopic Perspective. In Pre-Columbian Foodways: Interdisciplinary Approaches to Food, Culture, and Markets in Ancient Mesoamerica, edited by J. E. Staller and M. D. Carrasco, pp. 399–420. Springer, New York. Fry, J. 2009 How to Cook a Tapir: A Memoir of Belize. University of Nebraska Press, Lincoln and London. Galán, A. B., M. Rodríguez, S. de Juana and M. Domínguez-Rodrigo 2009 A New Experimental Study on Percussion Marks and Notches and their Bearing on the Interpretation of Hammerstone-Broken Faunal Assemblages. Journal of Archaeological Science 36:776–784. Garber, J. F., M. K. Brown, J. J. Awe and C. J. Hartman 2004a Middle Formative Prehistory of the Central Belize Valley: An Examination of Architecture, Material Culture, and Sociopolitical Change at Blackman Eddy. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological 175 Research, edited by J. F. Garber, pp. 25–47. University Press of Florida, Gainesville. Garber, J. F., M. K. Brown, W. D. Driver, D. M. Glassman, C. J. Hartman, F. K. Reilly and L. Sullivan 2004b Archaeological Investigations at Blackman Eddy. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological Research, edited by J. F. Garber, pp. 48–85. University Press of Florida, Gainesville. Gee, K. L., J. H. Holman, M. K. Causey, A. N. Rossi and J. B. Armstrong 2002 Aging White-Tailed Deer by Tooth Replacement and Wear: A Critical Evaluation of a Time-Honored Technique. Wildlife Society Bulletin 30:387–393. Geist, V. 1994 Origin of the Species. In Deer, edited by D. Gerlach, S. Atwater and J. Schnell, pp. 2–16. Stackpole Books, Mechanicsburg. 1998 Deer of the World. Stackpole Books, Mechanicburg. Gifford, J. C. 1976 Prehistoric Pottery Analysis and the Ceramics of Barton Ramie in the Belize Valley. Memoirs of the Peabody Museum of Archaeology and Ethnology Vol. 18. Harvard University, Cambridge. Gilbert, F. F. and S. L. Slolt 1970 Variability in Aging Maine White-Tailed Deer by Tooth-Wear Characteristics. Journal of Wildlife Management 34:532–535. Gilbert, M. 1993 Mammalian Osteology. Missouri Archaeological Society, Columbia. Gilchrist, R. and H. C. Mytum 1986 Experimental Archaeology and Burnt Animal Bone from Archaeological Sites. Circaea 4:29–38. Gompper, M. E. 1995 Nasua narica. Mammalian Species 487:1–10. 1996 Sociality and Asociality in White-Nosed Coatis (Nasua narica): Foraging Costs and Benefits. Behavioral Ecology 7:254–263. Goodrich, C. and H. van der Schalie 1937 Mollusca of Petén and North Alta Vera Paz, Guatemala. University of Michigan Museum of Zoology Miscellaneous Publications 34. University of Michigan Press, Ann Arbor. 176 Götz, C. M. 2008 Coastal and Inland Patterns of Faunal Exploitation in the Prehispanic Northern Maya Lowlands. Quaternary International 191:154–169. 2009 ¡Venados para Todos!: Diferencias Socioeconómicas en el Uso de Animales Vertebrados en las Tierras Bajas Mayas del Norte. In XXII Simposio de Investigaciones Arqueológicas en Guatemala, 2008, edited by J. P. LaPorte, B. Arroyo and H. E. Mejía, pp. 873–889. Museo Nacional de Arqueología y Etnología, Guatemala. Graham, E. 1987 Resource Diversity in Belize and Its Implications for Models of Lowland Trade. American Antiquity 52:753–767. Grayson, D. K. 1978 Minimum Numbers and Sample Size in Vertebrate Faunal Analysis. American Antiquity 43:53–65. 1984 Quantitative Zooarchaeology: Topics in the Analysis of Archaeological Faunas. Academic Press, Orlando. Grayson, D. K. and F. Delpech 2008 The Large Mammals of Roc de Combe (Lot, France): The Châtelperronian and Aurignacian Assemblages. Journal of Anthropological Archaeology 27:338– 362. Grayson, D. K. and C. J. Frey 2004 Measuring Skeletal Part Representation in Archaeological Faunas. Journal of Taphonomy 2:27–42. Hamblin, N. L. 1984 Animal Use by the Cozumel Maya. University of Arizona Press, Tucson. 1985 The Role of Marine Resources in the Maya Economy: A Case Study from Cozumel, Mexico. In Prehistoric Lowland Maya Environment and Subsistence Economy, edited by M. D. Pohl, pp. 159–174. Papers of the Peabody Museum of Archaeology and Ethnology Vol. 77. Harvard University, Cambridge. Hammond, N. 2005 The Dawn and the Dusk: Beginning and Ending a Long-Term Research Program at the Preclassic Maya Site of Cuello, Belize. Anthropological Notebooks 11:45–60. 1991 Cuello: An Early Maya Community in Belize. Cambridge University Press, Cambridge. 177 Hammond, N. and J. C. Gerhardt 1990 Early Maya Architectural Innovation at Cuello, Belize. World Archaeology 21:461–481. Hammond, N. and S. Young 2003 Rango Social y Prácticas Funerarias Mayas : La Evidencia de Dieta y Ritual Durante el Preclásico en Cuello. In Antropología de la Eternidad : La Muerte en al Cultura Maya, edited by A. C. Ruiz, M. H. Ruiz and M. J. I. Ponce de León, pp. 279–297. Sociedad Española de Estudios Mayas, Madrid. Hansen, R. D. 1998 Continuity and Disjunction: The Pre-Classic Antecedents of Classic Maya Architecture. In Function and Meaning in Classic Maya Architecture, edited by S. D. Houston, pp. 49–122. Dumbarton Oaks, Washington, D.C. Harrigan, R. 2004 Mollusca of K’axob: For Supper and Soul. In K’axob: Ritual, Work, and Family in an Ancient Maya Village, edited by P. A. McAnany, pp. 399–412. Monumenta Archaeologica 22. Cotsen Institute of Archaeology, University of California, Los Angeles. Hather, J. G. and N. Hammond 1994 Ancient Maya Subsistence Diversity: Root and Tuber Remains from Cuello, Belize. Antiquity 68:330–335. Haynes, G. 1983a Frequencies of Spiral and Green-Bone Fractures on Ungulate Limb Bones in Modern Surface Assemblages. American Antiquity 48:102–114. 1983b A Guide to Differentiating Mammalian Carnivore Taxa Responsible for Gnaw Damage to Herbivore Limb Bones. Paleobiology 9:164–172. Healy, P. F. 1988 Music of the Maya. Archaeology 41(1):24–31. 1990a Excavations at Pacbitun, Belize: Preliminary Report on the 1986 and 1987 Investigations. Journal of Field Archaeology 17:247–262. 1990b An Early Classic Maya Monument at Pacbitun, Belize. Mexicon 12(6):109–110. 1992 The Ancient Maya Ballcourt at Pacbitun, Belize. Ancient Mesoamerica 3:229–239. 1999a Preclassic Maya of the Belize Valley: Some Observations (1999). In Belize Valley Preclassic Maya Project: Report on the 1996 and 1997 Field Seasons, 178 edited by P. F. Healy, pp. 83–102. Occasional Papers in Anthropology 13. Trent University, Peterborough. 1999b Radiocarbon Dates from Pacbitun, Belize: Results from the 1995 Field Season. In Belize Valley Preclassic Maya Project: Report on the 1996 and 1997 Field Seasons, edited by P. F. Healy, pp. 69–82. Occasional Papers in Anthropology 13. Trent University, Peterborough. 2006 Preclassic Maya of the Belize Valley: Key Issues and Questions. Research Reports in Belizean Archaeology 3:13–30. 1999c Belize Valley Preclassic Maya Project: Report on the 1996 and 1997 Field Seasons. Occasional Papers in Anthropology 13. Trent University, Peterborough. Healy, P. F. and J. J. Awe 1995a Preclassic Maya of the Belize Valley: 1994–1995 Project Research Objectives. In Belize Valley Preclassic Maya Project: Report on the 1994 Field Season, edited by P. F. Healy and J. J. Awe, pp. 1–17. Occasional Papers in Anthropology 10. Trent University, Peterborough. 1995b Belize Valley Preclassic Maya Project: Report on the 1994 Field Season. Occasional Papers in Anthropology 10. Trent University, Peterborough. 1996 Belize Valley Preclassic Maya Project: Report on the 1995 Field Season. Occasional Papers in Anthropology 12. Trent University, Peterborough. Healy, P. F., J. J. Awe and H. Helmuth 2004a Defining Royal Maya Burials. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological Research, edited by J. F. Garber, pp. 228–237. University of Florida Press, Gainesville. Healy, P. F., J. J. Awe, G. Iannone and C. Bill 1995 Pacbitun (Belize) and Ancient Maya Use of Slate. Antiquity 65:337–348. Healy, P. F., D. Cheetham, T. G. Powis and J. J. Awe 2004 Cahal Pech: The Middle Formative Period. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological Research, edited by J. F. Garber, pp. 101–124. University Press of Florida, Gainesville. Healy, P. F., K. F. Emery and L. E. Wright 1990 Ancient and Modern Maya Exploitation of the Jute Snail (Pachychilus). Latin American Antiquity 1:170–183. Healy, P. F., C. G. B. Helmke, J. J. Awe and K. S. Sunahara 2007 Survey, Settlement, and Population History at the Ancient Maya Site of Pacbitun, Belize. Journal of Field Archaeology 32:17–39. 179 Healy, P. F., B. Hohmann and T. G. Powis 2004b The Ancient Maya Center of Pacbitun. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological Research, edited by J. F. Garber, pp. 207–227. University Press of Florida, Gainesville. Helmke, C. G. B., N. Grube, J. J. Awe and P. F. Healy 2006 A Reinterpretation of Stela 6, Pacbitun, Belize. Mexicon 28(4):70–75. Henderson, H. H. 1998 The Organization of Staple Crop Production in Middle Formative, Late Formative, and Classic Period Farming Households at K’axob, Belize. Unpublished Ph.D. dissertation, Department of Anthropology, University of Pittsburgh, Pittsburgh. 2003 The Organization of Staple Crop Production at K’axob, Belize. Latin American Antiquity 14:469–496. Hester, T. R., H. J. Shafer and J. D. Eaton (editors) 1982 Archaeology at Colha, Belize: The 1981 Interim Report. Center for Archaeological Research, University of San Antonio, San Antonio. 1994 Continuing Archaeology at Colha, Belize. Studies in Archaeology No. 16. Texas Archaeological Research Laboratory, University of Texas, Austin. Higgins, J. 1999 Túnel: A Case Study of Avian Zooarchaeology and Taphonomy. Journal of Archaeological Science 26:1449–1457. Hill, K., K. Hawkes, M. Hurtado and H. Kaplan 1984 Seasonal Variance in the Diet of Ache Hunter-Gatherers in Eastern Paraguay. Human Ecology 12:101–135. Hill, K., H. Kaplan, K. Hawkes and A. M. Hurtado 1987 Foraging Decisions Among Aché Hunter-Gatherers: New Data and Implications for Optimal Foraging Models. Ethology and Sociobiology 8:1–36. Hillson, S. 2005 Teeth. 2nd ed. Cambridge University Press, Cambridge. Hirth, D. H. 1994 Does Behavior during Breeding Season. In Deer, edited by D. Gerlach, S. Atwater and J. Schnell, pp. 122–128. Stackpole Books, Mechanicsburg. Hofman, J. L. 1992 Putting the Pieces Together: An Introduction to Refitting. In Piecing Together the Past: Applications of Refitting Studies in Archaeology, edited by J. 180 L. Hofman and J. G. Enloe, pp. 1–20. BAR International Series 578. British Archaeological Reports, Oxford. Hohmann, B. and T. G. Powis 1996 The 1995 Excavations at Pacbitun, Belize: Investigations of the Middle Formative Occupation in Plaza B. In Belize Valley Preclassic Maya Project: Report on the 1995 Field Season, edited by P. F. Healy and J. J. Awe, pp. 98–127. Occasional Papers in Anthropology 12. Trent University, Peterborough. 1999 The 1996 Excavations at Plaza B at Pacbitun, Belize. In Belize Valley Preclassic Maya Project: Report on the 1996 and 1997 Field Seasons, edited by P. F. Healy, pp. 1–18. Occasional Papers in Anthropology 13. Trent University, Peterborough. Hohmann, B., T. G. Powis and C. Arendt 1999 The 1997 Investigations at Pacbitun, Belize. In Belize Valley Preclassic Maya Project: Report on the 1996 and 1997 Field Seasons, edited by P. F. Healy, pp. 19–29. Occasional Papers in Anthropology 13. Trent University, Peterborough. Hohmann, B. M. 2002 Preclassic Maya Shell Ornament Production in the Belize Valley, Belize. Unpublished Ph.D. dissertation, Department of Anthropology, University of New Mexico, Albuquerque. Holwitz, L. R. K. 1990 The Origin of Partially Digested Bones Recovered from Archaeological Contexts in Israel. Paléorient 16:97–106. Hopkins, M. R. 1992 Mammalian Remains. In Artifacts from the Cenote of Sacrifice, Chichen Itza, Yucatan, edited by C. C. Coggins, pp. 369–385. Peabody Museum of Archaeology and Ethnology, Harvard University, Cambridge. Hubbs, C. L. 1935 Fresh-Water Fishes Collected in British Honduras and Guatemala. University of Michigan Museum of Zoology Miscellaneous Publications 28. University of Michigan Press, Ann Arbor. Inomata, T., D. Triadan, K. Aoyama, V. Castillo and H. Yonenobu 2013 Early Ceremonial Constructions at Ceibal, Guatemala, and the Origins of Lowland Maya Civilization. Science 340:467–471. Jacobson, H. A. 1994 Reproduction. In Deer, edited by D. Gerlach, S. Atwater and J. Schnell, pp. 98–108. Stackpole Books, Mechanicsburg. 181 Johnson, E. 1985 Current Developments in Bone Technology. In Advances in Archaeological Method and Theory, edited by M. B. Schiffer, pp. 157–235 Vol. 8. Academic Press, New York. Johnston, K. J. 2006 Preclassic Maya Occupation of the Itzan Escarpment, Lower Río de la Pasión, Petén, Guatemala. Ancient Mesoamerica 17:177–201. Jones, E. L. 2006 Prey choice, mass collecting, and the wild European rabbit (Oryctolagus cuniculus). Journal of Anthropological Archaeology 25:275–289. Jones, J. G. 1994 Pollen Evidence for Early Settlement and Agriculture in Northern Belize. Palynology 18:205–211. Jorgenson, J. P. 1999 Wildlife Conservation and Game Harvest by Maya Hunters in Quintana Roo, Mexico. In Hunting for Sustainability in Tropical Forests, edited by J. G. Robinson and E. L. Bennett, pp. 251–266. Columbia University Press, New York. Kidder, A. V., J. D. Jennings and E. H. Shook 1946 Excavations at Kaminaljuyu, Guatemala. Carnegie Institution of Washington Publication 576. Carnegie Institution of Washington, Washington, D.C. Kirkpatrick, R. D. and L. K. Sowls 1962 Age Determination of the Collared Peccary by the Tooth-Replacement Pattern. Journal of Wildlife Management 26:214–217. Klein, R. G. and K. Cruz-Uribe 1984 The Analysis of Animal Bones from Archaeological Sites. University of Chicago Press, Chicago. Kroll, J. C. 1994 Internal Anatomy. In Deer, edited by D. Gerlach, S. Atwater and J. Schnell, pp. 24–31. Stackpole Books, Mechanicsburg. Lam, Y. M., X. Chen and O. M. Pearson 1999 Intertaxonomic Variability in Patterns of Bone Density and the Differential Representation of Bovid, Cervid, and Equid Elements in the Archaeological Record. American Antiquity 64:343–362. Lam, Y. M., O. M. Pearson, C. W. Marean and X. Chen 2003 Bone Density Studies in Zooarchaeology. Journal of Archaeological Science 30:1701–1708. 182 Lange, F. W. 1971 Marine Resources: A Viable Subsistence Alternative for the Prehistoric Lowland Maya. American Anthropologist 73:619–639. LaPorte, J. P. and V. Fialko 1995 Un Reencuentro con Mundo Perdido, Tikal, Guatemala. Ancient Mesoamerica 6:41–94. Lawlor, E., A. J. Graham and S. L. Fedick 1995 Preclassic Floral Remains from Cahal Pech, Belize. In Belize Valley Preclassic Maya Project, edited by P. F. Healy and J. J. Awe, pp. 150–172. Occasional Papers in Anthropology No. 10. Trent University, Peterborough. Lee, D. and J. J. Awe 1995 Middle Formative Architecture, Burials, and Craft Specialization: Report on the 1994 Investigations at the Cas Pek Group, Cahal Pech, Belize. In Belize Valley Preclassic Maya Project, edited by P. F. Healy and J. J. Awe, pp. 95–115. Occasional Papers in Anthropology No. 10. Trent University, Peterborough. Lentz, D. L. 1991 Maya Diets of the Rich and Poor: Paleoethnobotanical Evidence from Copan. Latin American Antiquity 2:269–287. 1999 Plant Resources of the Ancient Maya: The Paleoethnobotanical Evidence. In Reconstructing Ancient Maya Diet, edited by C. D. White, pp. 3–18. University of Utah Press, Salt Lake City. Lentz, D. L., M. D. Pohl and K. O. Pope 2005 Domesticated Plants and Cultural Connections in Early Mesoamerica: Formative Period Paleoethnobotanical Evidence from Belize, Mexico, and Honduras. In New Perspectives on Formative Mesoamerican Cultures, edited by T. G. Powis, pp. 121–126. BAR International Series 1377. Archaeopress, Oxford. Linares, O. F. 1976 “Garden Hunting” in the American Tropics. Human Ecology 4:331–349. Losey, R. J., V. L. Bazaliiskii, S. Garvie-Lok, M. Germonpré, J. A. Leonard, A. L. Allen, M. A. Katzenberg and M. V. Sablin 2011 Canids as persons: Early Neolithic dog and wold burials, Cis-Baikal, Siberia. Journal of Anthropological Archaeology 30(2):174–189. Lotze, J.-H. and S. Anderson 1979 Procyon Lotor. Mammalian Species 119:1–8. 183 Lubinski, P. M. 1996 Fish Heads, Fish Heads: An Experiment on Differential Bone Preservation in a Salmonid Fish. Journal of Archaeological Science 23:175–181. Lupo, K. D. 2007 Evolutionary Foraging Models in Zooarchaeological Analysis: Recent Applications and Future Challenges. Journal of Archaeological Research 15:143– 189. Luther, E. 1974 Analysis of Faunal Material. In Excavations at Actún Polbilche, Belize, edited by D. M. Pendergast, pp. 62–80. Archaeology Monograph 1. Royal Ontario Museum, Toronto. Lyman, R. L. 1982 Bone Density and Differential Survivorship of Fossil Classes. Journal of Anthropological Archaeology 3:259–299. 1994 Vertebrate Taphonomy. Cambridge University Press, Cambridge. 2008 Quantitative Paleozoology. Cambridge University Press, New York. Lyman, R. L. and M. J. O'Brien 1987 Plow-Zone Zooarchaeology: Fragmentation and Identifiability. Journal of Field Archaeology 14:493–498. MacArthur, R. H. and E. R. Pianka 1966 On Optimal Use of a Patchy Environment. The American Naturalist 100(916):603–609. Madrigal, T. C. 2004 The Derivation and Application of White-Tailed Deer Utility Indices and Return Rates. Journal of Taphonomy 2:185–199. Marchinton, R. L. 1994 Deer and Dogs. In Deer, edited by D. Gerlach, S. Atwater and J. Schnell, pp. 231–232. Stachpole Books, Mechanicsburg. Marcus, J. 1982 The Plant World of the Sixteenth- and Seventeenth-Century Lowland Maya. In Maya Subsistence: Studies in the Memory of Dennis E. Puleston, edited by K. V. Flannery, pp. 239–273. Academic Press, New York. Marean, C. W. 1991 Measuring the Post-Depositional Destruction of Bones in Archaeological Assemblages. Journal of Archaeological Science 18:677–694. 184 Marean, C. W., Y. Abe, P. J. Nilssen and E. C. Stone 2001 Estimating the Minimum Number of Skeletal Elements (MNE) in Zooarchaeology: A Review and a New Image-Analysis GIS Approach. American Antiquity 66:333–348. Marean, C. W. and S. Y. Kim 1998 Mousterian Large-Mammal Remains from Kobeh Cave: Behavioral Implications for Neanderthals and Early Modern Humans. Current Anthropology 39:S79–S114. Marean, C. W. and L. M. Spencer 1991 Impact of Carnivore Ravaging on Zooarchaeological Measures of Element Abundance. American Antiquity 56:645–658. Marshall, F. and T. Pilgram 1993 NISP vs. MNI in Quantification of Body-Part Representation. American Antiquity 58:261–269. Martín, F. M. and L. A. Borrero 1997 A Puma Lair in Southern Patagonia: Implications for the Archaeological Record. Current Anthropology 38:453–461. Masson, M. A. 1999 Animal Resource Manipulation in Ritual and Domestic Contexts at Postclassic Maya Communities. World Archaeology 31:93–120. Masson, M. A. 2004a Contribution of Fishing and Hunting to Subsistence and Symbolic Expression. In K’axob: Ritual, Work, and Family in an Ancient Maya Village, edited by P. A. McAnany, pp. 383–397. Monumenta Archaeologica 22. Cotsen Institute of Archaeology, University of California, Los Angeles. 2004b Fauna Exploitation from the Preclassic to the Postclassic Periods at Four Maya Settlements in Northern Belize. In Maya Zooarchaeology: New Directions in Method and Theory, edited by K. F. Emery, pp. 97–122. Monograph 51. Cotsen Institute of Archaeology, University of California, Los Angeles. Masson, M. A. and C. P. Lope 2008 Animal Use at the Postclassic Maya Center of Mayapán. Quaternary International 191:170–183. Mayer, J. J. and R. M. Wetzel 1987 Tayassu pecari. Mammalian Species 293:1–7. McBee, K. and R. J. Baker 1982 Dasypus novemcinctus. Mammalian Species 162:1–9. 185 McKillop, H. 1984 Prehistoric Maya Reliance on Marine Resources: Analysis of a Midden from Moho Cay, Belize. Journal of Field Archaeology 11:25–35. 1985 Prehistoric Exploitation of the Manatee in the Maya and Circum-Caribbean Areas. World Archaeology 16:337–353. 1996 Prehistoric Maya Use of Native Palms: Archaeobotanical and Ethnobotanical Evidence. In The Managed Mosaic: Ancient Maya Agriculture and Resource Use, edited by S. L. Fedick, pp. 278–294. University of Utah Press, Salt Lake City. 2004a The Ancient Maya: New Perspectives. W.W. Norton & Company, New York. 2004b The Classic Maya Trading Port of Moho Cay. In The Ancient Maya of the Belize Valley: Half a Century of Archaeological Research, edited by J. F. Garber, pp. 257–272. University Press of Florida, Gainesville. McManus, J. J. 1974 Didelphis virginiana. Mammalian Species 40:1–6. Méndez, E. 1984 Mexico and Central America. In White-Tailed Deer: Ecology and Management, edited by L. K. Halls, pp. 513–524. Stackpole Books, Harrisburg. Merwin, R. E. and G. C. Vaillant 1932 The Ruins of Holmul, Guatemala. Memoirs of the Peabody Museum of Archaeology and Ethnology Vol. 3, No. 2. Harvard University, Cambridge. Metcalfe, D. and K. R. Barlow 1992 A Model for Exploring the Optimal Trade-off between Field Processing and Transport. American Anthropologist 94:340–356. Metcalfe, D. and K. T. Jones 1988 A Reconsideration of Animal Body-Part Utility Indices. American Antiquity 53:486–504. Miksicek, C. H. 1991 The Ecology and Economy of Cuello. In Cuello: an Early Maya Community, edited by N. Hammond, pp. 70–84. Cambridge University Press, Cambridge. Miksicek, C. H., R. M. Bird, B. Pickersgill, S. Donaghey, J. Cartwright and N. Hammond 1981a Preclassic Lowland Maize from Cuello, Belize. Nature 289:56–59. 186 Miksicek, C. H., K. J. Elsesser, I. A. Wuebber, K. O. Bruhns and N. Hammond 1981b Rethinking Ramon: A Comment on Reina and Hill’s Lowland Maya Subsistence. American Antiquity 46:916–919. Moedano-Koer, H. 1946 Jaina: Un cementerio Maya. Revista Mexicana de Estudios Antropológicos 8:217–242. Moholy-Nagy, H. 1963 Shells and Other Marine Material from Tikal. Estudios de Cultura Maya 3:65–83. 1978 The Utilization of Pomacea Snails at Tikal, Guatemala. American Antiquity 43:65–73. 1985 The Social and Ceremonial Uses of Marine Molluscs at Tikal. In Prehistoric Lowland Maya Environment and Subsistence Economy, edited by M. D. Pohl, pp. 147–158. Papers of Peabody Museum of Archaeology and Ethnology Vol. 77. Harvard University, Cambridge. 1994 Tikal Material Culture: Artifacts and Social Structure at a Classic Lowland Maya City. Unpublished Ph.D. dissertation, Department of Anthropology, University of Michigan, Ann Arbor. 1998 A Preliminary Report on the Use of Vertebrate Fauna from Tikal, Guatemala. In Anatomía de una Civilización : Aproximaciones Interdisciplinarias a la Cultura Maya, edited by A. Ciudad Ruiz, M. Y. F. Marquínez, J. M. G. Campillo, M. J. I. Ponce de León, A. L. García-Gallo and L. T. S. Castro, pp. 115–129. Sociedad Española de Estudios Mayas, Madrid. Mondini, M. and A. S. Muñoz 2008 Pumas as Taphonomic Agents: A Comparative Analysis of Actualistic Studies in the Neotropics. Quaternary International 180:52–62. Montalvo, C. I., M. E. M. Pessino and M. E. González 2007 Taphonomic Analysis of Remains of Mammals Eaten by Pumas (Puma concolor, Carnivora, Felidae) in Central Argentina. Journal of Archaeological Science 34:2151–2160. Montero-Lopez, C. 2009 Sacrifice and Feasting Among the Classic Maya Elite, and the Importance of the White-Tailed Deer: Is There a Regional Pattern? . Journal of Historical and European Studies 2:53–68. Morin, E. 2007 Fat Composition and Nunamiut Decision-Making: A New Look at the Marrow and Bone Grease Indices. Journal of Archaeological Science 34:69–82. 187 2010 Taphonomic Implications of the Use of Bone as Fuel. Palethnologie 2:209–217. 2012 Reassessing Paleolithic Subsistence: The Neanderthal and Modern Human Foragers of Saint-Césaire. Cambridge University Press, Cambridge. Morin, E. and E. Ready 2013 Foraging Goals and Transport Decisions in Western Europe During the Paleolithic and Early Holocene. In Zooarchaeology and Modern Human Origins, edited by J. L. Clark and J. D. Speth, pp. 1–43. Springer, New York (in press). Morin, E., T. Tsanova, N. Sirakov, W. Rendu, J.-B. Mallye and F. Lévêque 2005 Bone Refits in Stratified Deposits: Testing the Chronological Grain at Saint-Césaire. Journal of Archaeological Science 32:1083–1098. Morlan, R. E. 1980 Taphonomy and Archaeology in the Upper Pleistocene of the Northern Yukon Territory: A Glimpse of the Peopling of the New World. National Museum of Man Mercury Series Paper No. 94. National Museums of Canada, Ottawa. 1994 Bison Bone Fragmentation and Survivorship: A Comparative Method. Journal of Archaeological Science 21:797–807. Muñoz, A. S., M. Mondini, V. Durán and A. Gasco 2008 Los Pumas (Puma concolor) como Agentes Tafonómicos. Análisis Actualístico de un Sitio de Matanza en los Andes de Mendoza, Argentina. Geobios 41:123–131. Murie, A. M. 1935 Mammals from Guatemala and British Honduras. University of Michigan Museum of Zoology Miscellaneous Publication 26. University of Michigan Press, Ann Arbor. Nicholson, R. A. 1993 A Morphological Investigation of Burnt Animal Bone and an Evaluation of Its Utility in Archaeology. Journal of Archaeological Science 20:411–428. 1996 Bone Degradation, Burial Medium and Species Representation: Debunking the Myths, an Experiment-Based Approach. Journal of Archaeological Science 23:513–533. Ojasti, J. 1996 Wildlife Utilization in Latin America: Current Situation and Prospects for Sustainable Management. FAO Conservation Guide 25. Food and Agriculture Organization of the United Nations, Rome. 188 Oliveira, F. S. and J. C. Canola 2007 Erupção Dental em Pacas (Agouti paca) Criadas em Cativeiro. Arquivo Brasileiro de Medicina Veterinária e Zootecnia 59(2):390–394. Olsen, S. J. 1972 Animal Remains from Altar de Sacrificios. In The Artifacts of Altar de Sacrificios, edited by G. R. Willey, pp. 243–246. Papers of the Peabody Museum of Archaeology and Ethnology Vol. 64, No. 1. Harvard University, Cambridge. 1978 Vertebrate Faunal Remains. In Excavations at Seibal, Department of Petén, Guatemala, edited by G. R. Willey, pp. 172–176. Memoirs of the Peabody Museum of Anthropology and Ethnology Vol. 14, No. 1. Harvard University, Cambridge. 1982 An Osteology of Some Maya Mammals. Papers of the Peabody Museum of Archaeology and Ethnology 73. Harvard University Press, Cambridge. Orians, G. H. and N. E. Pearson 1979 On the Theory of Central Place Foraging. In Analysis of Ecological Systems, edited by D. J. Horn, G. R. Stairs and R. D. Mitchell, pp. 155–177. Ohio State University Press, Columbus. Payne, S. 1973 Kill-Off Patterns in Sheep and Goats: The Mandibles from Aşvan Kale. Anatolian Studies 23:281–303. 1975 Partial Recovery and Sample Bias. In Archaeozoological Studies, edited by A. T. Clason, pp. 7–17. American Elsevier, New York. Pendergast, D. 1979 Excavations at Altun Ha, Belize, 1964–1970, Volume 1. Royal Ontario Museum, Toronto. Pérez, E. M. 1992 Agouti paca. Mammalian Species 404:1–7. Pickering, T. R. and C. P. Egeland 2006 Experimental Patterns of Hammerstone Percussion Damage on Bones: Implications for Inferences of Carcass Processing by Humans. Journal of Archaeological Science 33:459–469. Pina-Chan, R. 1968 Jaina: La Casa en el Agua. Instituto Nacional de Antropología e Historia, Mexico City. 189 Plug, C. and I. Plug 1990 MNI counts as Estimates of Species Abundance. The South African Archaeological Bulletin 45(151):53–57. Pohl, M. D. 1976 Ethnozoology of the Maya: An Analysis of Fauna from Five Sites in the Peten, Guatemala. Unpublished Ph.D. dissertation, University of Pennsylvania, Philadelphia. 1981 Ritual Continuity and Transformation in Mesoamerica: Reconstructing the Ancient Maya Cuch Ritual. American Antiquity 46:513–529. 1983 Maya Ritual Faunas: Vertebrate Remains from Burials, Caches, and Cenotes in the Maya Lowlands. In Civilization of the Ancient Americas: Essays in Honor of Gordon R. Willey, edited by R. M. Leventhal and A. L. Kolata, pp. 55– 103. University of New Mexico Press, Albuquerque. 1990 The Ethnozoology of the Maya: Faunal Remains from Five Sites in Peten, Guatemala. In Excavations at Seibal, edited by G. R. Willey, pp. 143–174. Memoirs of the Peabody Museum of Archaeology and Ethnology Vol. 1–4. Harvard University, Cambridge. 1994 Late Classic Maya Fauna from Settlement in the Copan Valley, Honduras: Assertion of Social Status through Animal Consumption. In Ceramics and Artifacts from Excavations in the Copan Residential Zone, edited by A. A. Demarest and W. L. Fash. Papers of the Peabody Museum of Archaeology and Ethnology Vol. 80. Harvard University, Cambridge. Pohl, M. D. and L. H. Feldman 1982 The Traditional Role of Women and Animals in Lowland Maya Economy. In Maya Subsistence: Studies in the Memory of Dennis E. Puleston, edited by K. V. Flannery, pp. 295–311. Academic Press, New York. Pohl, M. D., K. O. Pope, J. G. Jones, J. S. Jacob, D. R. Piperno, S. D. deFrance, D. L. Lentz, J. A. Gifford, M. E. Danforth and J. K. Josserand 1996 Early Agriculture in the Maya Lowlands. Latin American Antiquity 7:355– 372. Powis, T. G. 2004 Ancient Lowland Maya Utilization of Freshwater Pearly Mussels (Nephronaias spp.). In Maya Zooarchaeology: New Directions in Method and Theory, edited by K. F. Emery, pp. 125–140. Monograph 51. Cotsen Institute of Archaeology, Los Angeles. 2005 Formative Mesoamerican Cultures: An Introduction. In New Perspectives on Formative Mesoamerican Cultures, edited by T. G. Powis, pp. 1–14. BAR International Series 1377. Archaeopress, Oxford. 190 2009 Pacbitun Preclassic Project: Report on the 2008 Field Season. Report submitted to the Institute of Archaeology, National Institute of Culture and History, Belmopan, Belize. 2010 Pacbitun Preclassic Project: Report on the 2009 Field Season. Report submitted to the Institute of Archaeology, National Institute of Culture and History, Belmopan, Belize. 2011 Preliminary Investigations into Sub-Plaza Deposits in Plaza A at Pacbitun, Belize. In Pacbitun Regional Archaeological Project (PRAP): Report on the 2010 Field Season, edited by T. G. Powis, pp. 142–151. Report submitted to the Institute of Archaeology, National Institute of Culture and History, Belmopan, Belize. 2012 Pacbitun Regional Archaeological Project (PRAP): Report on the 2010 Field Season. Report submitted to the Institute of Archaeology, National Institute of Culture and History, Belmopan, Belize. Powis, T. G., J. J. Awe, P. F. Healy and N. Stanchly 2002 La Explotación de Recursos Animales por los Antiguos Mayas del Periodo Formativo Medio : Nueva Evidencia del Grupo Tolok en Cahal Pech. In Memorias del Tercer Congreso Internacional de Mayistas, 1995, edited by A. L. Izquierdo y de la Cueva, pp. 505–518. Instituto de Investigaciones Filológicas y Centro de Estudios Mayas, Universidad Autónoma de México, Mexico City. Powis, T. G., N. Stanchly, C. D. White, P. F. Healy, J. J. Awe and F. Longstaffe 1999 A Reconstruction of Middle Preclassic Subsistence Economy at Cahal Pech, Belize. Antiquity 73:364–376. Presley, S. J. 2000 Eira barbara. Mammalian Species 636:1–6. Puleston, D. E. 1982 The Role of Ramón in Maya Subsistence. In Maya Subsistence: Studies in the Memory of Dennis E. Puleston, edited by K. V. Flannery, pp. 353–366. Academic Press, New York. Purdue, J. R. 1983 Epiphyseal Closure in White-Tailed Deer. Journal of Wildlife Management 47:1207–1213. Reid, F. A. 2009 A Field Guide to the Mammals of Central America and Southeast Mexico. 2nd ed. Oxford University Press, New York. 191 Reitz, E. J. and E. S. Wing 2008 Zooarchaeology. 2nd ed. Cambridge University Press, New York. Repoussard, A. 2009 Stable Carbon and Oxygen Isotopes in Bone: Tracing Droughts during the Maya Era Using Archaeological Deer Remains. Unpublished M.A. thesis, School of Geography and Earth Sciences, McMaster University, Hamilton. Richie, C. F. 1990 Ancient Maya Settlement and Environment of the Eastern Zone of Pacbitun, Belize. Unpublished M.A. thesis, Department of Anthropology, Trent University, Peterborough. Ricketson, E. B. 1937 The Artifacts. In Uaxactún, Guatemala: Group E––1926–1931, edited by O. G. J. Ricketson and E. B. Ricketson, pp. 204–208. Carnegie Institution of Washington, Washington, D. C. Ringrose, T. J. 1993 Bone Counts and Statistics: A Critique. Journal of Archaeological Science 20:121–157. Rissolo, D., J. M. Ochoa Rodriguez and J. W. Ball 2005 A Reassessment of the Middle Preclassic in Northern Quintana Roo. In Quintana Roo Archaeology, edited by J. M. Shaw and J. P. Mathews, pp. 66–77. University of Arizona Press, Tucson. Roys, R. L. 1931 The Ethno-Botany of the Maya. Middle American Research Series No. 2. Tulane University, New Orleans. Savage, H. G. 1971 Faunal Material. In Excavations at Eduardo Quiroz Cave, British Honduras (Belize), edited by D. M. Pendergast, pp. 78–110. Art and Archaeology Occasional Papers 21. Royal Ontario Museum, Toronto. Schlesinger, V. 2001 Animals and Plants of the Ancient Maya: A Guide. University of Texas Press, Austin. Schoener, T. W. 1979 Generality of the Size-Distance Relation in Models of Optimal Feeding. The American Naturalist 114:902–914. Serjeantson, D. 2009 Birds. Cambridge University Press, Cambridge. 192 Severinghaus, C. W. 1949 Tooth Development and Wear as Criteria of Age in White-Tailed Deer. Journal of Wildlife Management 13:315–321. Seymour, K. L. 1989 Panthera onca. Mammalian Species 340:1–9. Shaffer, B. S. 1992 Quarter-Inch Screening: Understanding Biases in Recovery of Vertebrate Faunal Remains. American Antiquity 57:129–136. Shaffer, B. S. and J. L. J. Sanchez 1994 Comparison of 1/8″- and 1/4″-Mesh Recovery of Controlled Samples of Small-to-Medium-Sized Mammals. American Antiquity 59:525–530. Sharer, R. J. 1994 The Ancient Maya. 5th ed. Stanford University Press, Stanford. Shaw, L. C. 1991 The Articulation of Social Inequality and Faunal Resource Use in the Preclassic Community of Colha, Northern Belize. Unpublished Ph.D. dissertation, Department of Anthropology, University of Massachusetts, Amherst. 1999 Social and Ecological Aspects of Preclassic Maya Meat Consumption at Colha, Belize. In Reconstructing Ancient Maya Diet, edited by C. D. White, pp. 83–100. University of Utah Press, Salt Lake City. Sheffield, S. R. and H. H. Thomas 1997 Mustela frenata. Mammalian Species 570:1–9. Shipman, P., G. Foster and M. Schoeninger 1984 Burnt Bones and Teeth: An Experimental Study of Color, Morphology, Crystal Structure and Shrinkage. Journal of Archaeological Science 11:307–325. Silver, I. A. 1969 The Ageing of Domestic Animals. In Science in Archaeology: A Survey of Progress and Research, edited by D. Brothwell, E. Higgs and C. Grahame, pp. 283–302. Thames and Hudson, London. Smith, E. A. 1983 Anthropological Applications of Optimal Foraging Theory: A Critical Review. Current Anthropology 24:625–651. Snow, D. H. 1969 Late Classic Maya Occupation in the San Antonio (Cayo District) SubRegion, Western British Honduras. Katunob 7(1):47–49. 193 Soibelzon, E., M. Medina and A. M. Abba 2012 Late Holocene armadillos (Mammalia, Dasypodidae) of the Sierras of Córdoba, Argentina: Zooarchaeology, diagnostic characters and their paleozoological relevance. Quaternary International http://dx.doi.org/10.1016/j.quaint.2012.09.009. Solis, W. 2011 Ancient Maya Exploitation of Jute (Pachychilus spp.) at Minanha, West Central Belize. Unpublished M.A. thesis, Department of Anthropology, Trent University, Peterborough. Spenard, J. 2011 Heading to the Hills: A Preliminary Reconnaissance Report on Pacbitun’s Regional Landscape. In Pacbitun Regional Archaeological Project (PRAP): Report on the 2010 Field Season, edited by T. G. Powis, pp. 33–89. Report submitted to the Institute of Archaeology, National Institute of Culture and History, Belmopan, Belize. Stanchly, N. 1995 Formative Period Maya Faunal Utilization at Cahal Pech, Belize: Preliminary Analysis of the Animal Remains from the 1994 Field Season. In Belize Valley Preclassic Maya Project: Report on the 1994 Field Season, edited by P. F. Healy and J. J. Awe, pp. 124–149. Occasional Papers in Anthropology 10. Trent University, Peterborough. 1999 Preliminary Report on the Preclassic Faunal Remains from Pacbitun, Belize: 1995 and 1996 Field Seasons. In Belize Valley Preclassic Maya Project: Report on the 1996 and 1997 Field Seasons, edited by P. F. Healy, pp. 41–52. Occasional Papers in Anthropology 13. Trent University, Peterborough. 2004 Picks and Stones May Break My Bones: Taphonomy and Maya Zooarchaeology. In Maya Zooarchaeology: New Directions in Method and Theory, edited by K. F. Emery, pp. 35–43. Monograph 51. Cotsen Institute of Archaeology, Los Angeles. Stanchly, N. and J. Dale 1992 An Analysis of the Faunal Remains from Structure B-4, Units 4 and 5, Cahal Pech, Belize. In Progress Report of the Fourth Season (1991) of Investigations at Cahal Pech, Belize, edited by J. J. Awe and M. D. Campbell, pp. 141–167. Department of Anthropology, Trent University, Peterborough. Stanton, T. W. and T. Ardren 2005 The Middle Formative of Yucatan in Context. Ancient Mesoamerica 16:213–228. Stephens, D. W. and J. R. Krebs 1986 Foraging Theory. Princeton University Press, Princeton. 194 Stiner, M. C. 1994 Honor among Thieves: A Zooarchaeological Study of Neandertal Ecology. Princeton University Press, Princeton. Stiner, M. C., S. L. Kuhn, S. Weiner and O. Bar-Yosef 1995 Differential Burning, Recrystallization, and Fragmentation of Archaeological Bone. Journal of Archaeological Science 22:223–237. Stiner, M. C., N. D. Munro and T. A. Surovell 2000 The Tortoise and the Hare: Small-Game Use, the Broad-Spectrum Revolution, and Paleolithic Demography. Current Anthropology 41:39–79. Stuart, L. C. 1935 A Contribution to a Knowledge of the Herpetology of a Portion of the Savanna Region of Central Petén, Guatemala. Miscellaneous Publications No. 29. Museum of Zoology, University of Michigan Press, Ann Arbor. 1964 Fauna of Middle America. In Handbook of Middle American Indians Vol. 1, edited by R. C. West and R. Wauchope, pp. 316–362. University of Texas Press, London. Sunahara, K. S. 1995 Ancient Maya Settlement: The Western Zone of Pacbitun, Belize. Unpublished M.A. thesis, Department of Anthropology, Trent University, Peterborough. Tappen, M. 1994 Bone Weathering in the Tropical Rain Forest. Journal of Archaeological Science 21:667–673. Teeter, W. G. 2001 Maya Animal Utilization in a Growing City: Vertebrate Exploitation at Caracol, Belize. Unpublished Ph.D. dissertation, Department of Anthropology, University of California, Los Angeles. Tewes, M. E. and D. J. Schmidly 1987 The Neotropical Felids: Jaguar, Ocelot, Margay, and Jaguarundi. In Wild Furbearer Management and Conservation in North America, edited by M. Novak and J. Baker, pp. 697–711. Ontario Ministry of Natural Resources, Toronto. Thornton, E. K. 2011 Reconstructing Ancient Maya Animal Trade through Strontium Isotope (87Sr/86Sr) Analysis. Journal of Archaeological Science 38:3254–3263. 195 Thurston, E. B. 2011 Crocodiles and the Ancient Maya: An Examination of the Iconographic and Zooarchaeological Evidence. Unpublished M.A. thesis, Department of Anthropology, Trent University, Peterborough. Todd, L. C. and D. J. Rapson 1988 Long Bone Fragmentation and Interpretation of Faunal Assemblages: Approaches to Comparative Analysis. Journal of Archaeological Science 15:307– 325. Todd, L. C. and D. J. Stanford 1992 Application of Conjoined Bone Data to Site Structural Studies. In Piecing Together the Past: Applications of Refitting Studies in Archaeology, edited by J. L. Hofman and J. G. Enloe, pp. 21–35. BAR International Series 578. British Archaeological Reports, Oxford. Tozzer, A. M. 1941 Landa’s Relación de las Cosas de Yucatan. Papers of the Peabody Museum of American Archaeology and Ethnology Vol. 18. Harvard University, Cambridge. Tozzer, A. M. and G. M. Allen 1910 Animal Figures in the Maya Codices. Papers of the Peabody Museum of American Archaeology and Ethnology Vol. 4, No. 3. Harvard University, Cambridge. Turner, B. L. and C. H. Miksicek 1984 Economic Plant Species Associated with Prehistoric Agriculture in the Maya Lowlands. Economic Botany 38:179–193. Tykot, R. H. 2002 Contribution of Stable Isotope Analysis to Understanding Dietary Variation among the Maya. In Archaeological Chemistry: Material, Methods, and Meaning, edited by K. A. Jakes, pp. 214–230. ACS Symposium Series 831. American Chemistry Society, Washington, D.C. Tykot, R. H., N. J. van der Merwe and N. Hammond 1996 Stable Isotope Analysis of Bone Collagen, Bone Apatite, and Tooth Enamel in the Reconstruction of Human Diet: A Case Study from Cuello, Belize. In Archaeological Chemistry: Organic, Inorganic, and Biochemical Analysis, edited by M. V. Orna, pp. 355–365. ACS Symposium Series 625. American Chemistry Society, Washington, D.C. Ugan, A. and S. Simms 2012 On Prey Mobility, Prey Rank, and Foraging Goals. American Antiquity 77:179–185. 196 Ungar, P. S. 2010 Mammal Teeth: Origin, Evolution, and Diversity. John Hopkins University Press, Baltimore. Vail, G. and A. Aveni 2004 Research Methodologies and New Approaches to Interpreting the Madrid Codex. In The Madrid Codex: New Approaches to Understanding an Ancient Maya Manuscript, edited by G. Vail and A. Aveni, pp. 1–30. University Press of Chicago, Boulder. Valdez, F. 1995 Religion and Iconography of the Preclassic Maya at Rio Azul, Peten, Guatemala. In Religión y Sociedad en el Area Maya, edited by C. Varela Torrecilla, J. L. Bonor and M. Y. Fernández Marquínez, pp. 211–218. Sociedad Española de Estudios Mayas, Madrid. Valdez, S. V., J. B. Lee, A. Wittke and A. Vaughan 2011 Excavations at Two Sites Within the Pacbitun Cave System: Report on the 2010 Season of the Pacbitun Regional Archaeological Project. In In Pacbitun Regional Archaeological Project (PRAP): Report on the 2010 Field Season, edited by T. G. Powis, pp. 19–32. Report submitted to the Institute of Archaeology, National Institute of Culture and History, Belmopan, Belize. van der Merwe, N. J., R. H. Tykot, N. Hammond and K. Oakberg 2000 Diet and Animal Husbandry of the Preclassic Maya at Cuello, Belize: Isotopic and Zooarchaeological Evidence. In Biogeochemical Approaches to Paleodietary Analysis, edited by S. H. Ambrose and M. A. Katzenberg, pp. 23–38. Advances in Archaeological and Museum Science Vol. 5. Kluwer Academic/Plenum, New York. van Tyne, J. 1935 The Birds of the Northern Petén. University of Michigan Museum of Zoology Miscellaneous Publications 27. University of Michigan Press, Ann Arbor. Verme, L. J. and D. E. Ullrey 1984 Physiology and Nutrition. In White-Tailed Deer: Ecology and Management, edited by L. K. Halls, pp. 91–118. Stackpole Books, Harrisburg. Villa, P., J.-C. Castel, C. Beauval, V. Bourdillat and P. Goldberg 2004 Human and Carnivore Sites in the European Middle and Upper Paleolithic: Similarities and Differences in Bone Modification and Fragmentation. Revue de Paléobiologie 23:705–730. Villa, P. and E. Mahieu 1991 Breakage Patterns of Human Long Bones. Journal of Human Evolution 21:27–48. 197 Villa, P., E. Soto, M. Santonja, A. Pérez-González, R. Mora, J. Parcerisas and C. Sesé 2005 New Data on Ambrosa: Closing the Hunting versus Scavenging Debate. Quaternary International 126–128:223–250. Wake, T. A. 2004a On the Paramount Importance of Adequate Comparative Collections and Recovery Techniques in the Identification and Interpretation of Vertebrate Archaeofaunas: A Reply to Vale & Gargett (2002). Archaeofauna 13:173–182. 2004b A Vertebrate Archaeofauna from the Early Formative Period Site of Paso de la Amada, Chiapas, Mexico: Preliminary Results. In Maya Zooarchaeology: New Directions in Method and Theory, edited by K. F. Emery, pp. 209–222. Monograph 51. Cotsen Institute of Archaeology, Los Angeles. Weber, J. 2011 Investigating the Ancient Maya Landscape: A Settlement Survey in the Periphery of Pacbitun. Unpublished M.A. thesis, Department of Anthropology, Georgia State University, Atlanta. Weber, J. U. and T. G. Powis 2011 The Role of Caves at Pacbitun: Peripheral to the Site Center or Central to the Periphery? . Research Reports in Belizean Archaeology 8:198–207. Wheeler, A. and A. G. K. Jones 1989 Fishes. Cambridge University Press, Cambridge. White, C. D. 1997 Ancient Diet at Lamanai and Pacbitun: Implications for the Ecological Model of Collapse. In Bones of the Maya: Studies of Ancient Skeletons, edited by S. L. Whittington and D. M. Reed, pp. 171–180. Smithsonian Institution Press, Washington, D.C. 2004 Stable Isotopes and the Human-Animal Interface in Maya Biosocial and Environmental Systems. Archaeofauna 13:183–198. White, C. D., P. F. Healy and H. P. Schwarcz 1993 Agriculture, Social Status, and Maya Diet at Pacbitun, Belize. Journal of Anthropological Research 49:347–375. White, C. D., D. M. Pendergast, F. J. Longstaffe and K. R. Law 2001a Social Complexity and Food Systems at Altun Ha, Belize: The Isotopic Evidence. Latin American Antiquity 12:371–393. White, C. D., M. D. Pohl, H. P. Schwarcz and F. J. Longstaffe 2001b Isotopic Evidence for Maya Patterns of Deer and Dog Use at Preclassic Colha. Journal of Archaeological Science 28:89–107. 198 White, C. D. and H. P. Schwarcz 1989 Ancient Maya Diet: As Inferred from Isotopic and Elemental Analysis of Human Bone. Journal of Archaeological Science 16:451–474. Wiesen, A. and D. L. Lentz 1999 Preclassic Floral Remains at Cahal Pech and Pacbitun, Belize: Summary Report. In Belize Valley Preclassic Maya Project: Report on the 1996 and 1997 Field Seasons, edited by P. F. Healy, pp. 53–67. Occasional Papers in Anthropology 13. Trent University, Peterborough. Willey, G. R. 1978 Bone and Related Artifacts. In Excavations at Seibal, edited by G. R. Willey, pp. 168–171. Memoirs of the Peabody Museum of Archaeology and Ethnology Vol. 14, No. 1–3. Harvard University, Cambridge. Willey, G. R., W. R. Bullard Jr., J. B. Glass and J. C. Gifford 1965 Prehistoric Maya Settlements in the Belize Valley. Papers of the Peabody Museum of Archaeology and Ethnology Vol. 54. Peabody Museum, Cambridge. Wing, E. S. 1975 Animal Remains from Lubaantún, Guatemala. In Lubaatún: A Classic Maya Realm, edited by N. Hammond, pp. 379–383. Peabody Museum of Archaeology and Ethnology Monograph 2. Harvard University, Cambridge. 1980 Vertebrate Faunal Remains from Dzibilchaltun. In Excavations at Dzibilchaltun, Yucatan, Mexico, edited by E. W. Andrews IV and E. W. Andrews V, pp. 326–331. Publication 48. Middle American Research Institute, Tulane University, New Orleans. Wing, E. S. and S. Scudder 1991 The Ecology and Economy of Cuello: The Exploitation of Animals. In Cuello: An Early Maya Community in Belize, edited by N. Hammond, pp. 84–97. Cambridge University Press, Cambridge. Winterhalder, B. and D. J. Kennett 2006 Behavioral Ecology and the Transition from Hunting and Gathering to Agriculture. In Behavioral Ecology and the Transition to Agriculture, edited by D. J. Kennett and B. Winterhalder, pp. 1–20. University of California Press, Berkeley. Wolverton, S., L. Nagaoka, J. Densmore and B. Fullerton 2008 White-Tailed Deer Harvest Pressure and Within-Bone Nutrient Exploitation during the Mid- to Late Holocene in Southeast Texas. Before Farming 2008/2, article 3:1–22. 199 Woodbury, R. B. and A. S. Trik 1954 The Ruins of Zaculeu, Guatemala. United Fruit Company, William Byrd Press, New York. Wright, A. C. S., D. H. Romney, R. H. Arbuckle and V. E. Rial 1959 Land in British Honduras: A Report of the British Honduras Land Use Survey Team. Colonial Research Publications No. 24. Her Majesty’s Stationery Office, London. Wright, L. E. 1997 Ecology or Society? Paleodiet and the Collapse of the Pasión Maya Lowlands. In Bones of the Maya: Studies of Ancient Skeletons, edited by S. L. Whittington and D. M. Reed, pp. 181–195. Smithsonian Institution Press, Washington, D. C. 2006 Diet, Health, and Status among the Pasión Maya: A Reappraisal of the Collapse. Vanderbilt Institute of Mesoamerican Archaeology Series Vol. 2. Vanderbilt University Press, Nashville. Young, S. 2002 Metabolic Mechanisms and the Isotopic Investigation of Ancient Diets with an Application to Human Remains from Cuello, Belize. Unpublished Ph.D. dissertation, Department of Anthropology, Harvard University, Cambridge. Zohar, I., T. Dayan, E. Galili and E. Spanier 2001 Fish Processing During the Early Holocene: A Taphonomic Case Study from Coastal Israel. Journal of Archaeological Science 28:1041–1053. 200 APPENDIX A Pacbitun faunal datasets by time period 201 ABBREVIATIONS Identification Code Scientific name Common name ART CER ODO MAZ TAY TAP CAN DOG COA MUS ARM OPOV OPOM CAT JAG PUM OCE MAR GOP DAS PAC AGO RAB AVES GAL COL VIP IGU TES KIN FISH ICT SER PAF BUF STM MTM LTM UNIM UNI Artiodactyla Cervidae Odocoileus virginianus Mazama americana Tayassuidae Tapirus bairdii Canidae Canis lupus familiaris Nasua narica Mustela frenata Dasypus novemcinctus Didelphis virginiana Didelphis marsupialis Felidae Panthera onca Puma concolor Leopardus pardalis Leopardus wiedii Orthogeomys spp. Dasyproctidae Cuniculus paca Dasyprocta punctata Sylvilagus spp. Aves Galliformes Colubridae Viperidae Iguanidae Testudines Kinosternon spp. Unidentified fish Ictaluridae Serranidae Sparisoma spp. Rhinella marinus Small terrestrial mammal Medium terrestrial mammal Large terrestrial mammal Indeterminate mammal Indeterminate specimen Artiodactyls Cervids White-tailed deer Red brocket deer Peccaries Baird’s tapir Canids Domestic dog Coatimundi Weasel Armadillo Virginia opossum Common opossum Cats Jaguar Puma Ocelot Margay Pocket gophers Agouti, paca Paca Agouti Rabbits Birds Turkey, guan Colubrid Vipers Iguanas Turtles Mud turtle Catfish Grouper Parrotfish Marine toad 202 Bone element ANT SKL FRN OCC NAS PAR PET ROS TEM ZYG PMX MAN MAX IN CN PM MO DP TTH HYD Antler fragment Skull fragment Frontal Occipital Nasal Parietal Petrous (bulla) Rostrum Temporal Zygomatic Premaxilla Mandible Maxilla Incisor Canine Premolar Molar Deciduous premolar Tooth fragment Hyoid ATL AXI CEV TRV LMV CDV VER SAC STX RIB CC Atlas Axis Cervical vertebra Thoracic vertebra Lumbar vertebra Caudal vertebra Vertebral fragment Sacrum Sternum Rib Coastal cartilage SCA HUM RAD RUL ULN CAP HAM LUN PIS SCP TRQ Scapula Humerus Radius Radius-ulna Ulna Capitatum Hamatum Lunate Pisiform Scaphoid Triquetrum ILM INN ISH PUB PAT FEM TIB FIB TFB AST CAL CUB GC MAL NAV SC NVB SES MTC MTP MTT PH1 PH2 PH3 PHA SHL DRS LBF UNI Ilium Innominate fragment Ischium Pubis Patella Femur Tibia Fibula Tibia-fibula Astragalus Calcaneus Cuboid Greater cuneiform Malleolar Navicular Smaller cuneiform Naviculo-cuboid Sesamoid Metacarpal Metapodial Metatarsal Phalanx 1 Phalanx 2 Phalanx 3 Phalanx fragment Shell Dorsal spine Long bone fragment Unidentified bone element SYN TBT CMT TMT PPX DPX UNG RNG FUR COR LSA QUA SCL CUN Synsacrum Tibiotarsus Carpometacarpus Tarsometatarsus Proximal phalanx (wing) Distal phalanx (wing) Ungus (talon) Tracheal ring Furcula Coracoid Lumbosacral Quadrate Scapholunar Cuneiform 203 End PE PS MS DS DE ANT POST CRA CAU UP LO ACE CEN W W-S S F Proximal end Proximal shaft Middle shaft Distal shaft Distal end Anterior Posterior Cranial Caudal Upper tooth Lower tooth Acetabulum Centrum (vertebra) Whole Fish vertebra with intact centrum but lacking all spines Shaft fragment Fragment Side L R AX Left Right Axial element Fusion FU U I Fused Unfused Intermediate (fused by line clearly visible) Only for deer teeth FAW Fawn: <1 year old YEA Yearling: 1–2 years old ADU Adult: >2 years old Max length <1 1–2 2–3 3–4 4–5 measuring less than 1 cm measuring between 1.00–1.99 cm measuring between 2.00–2.99 cm measuring between 3.00–3.99 cm measuring between 4.00–4.99 cm Surface state PO DA SD IT Poor Damaged Slightly damaged Intact 204 Taphonomy CRK RT EX SH STG CT PN DR BUR GN Cracking Root Exfoliation Sheeting Staining Cut mark Percussion notch Drilled Burned Gnawing Table A.1 Pacbitun dataset for the early Middle Preclassic period Catalogue number Side Count Fusion Max length Max width Surface state Plaza Unit Level ID Bone End PAC-08BO-014-01 B 1 6 UNIM UNI F 3 <1 DA EX PAC-08BO-014-02 B 1 6 UNIM UNI F 5 1–2 DA EX PAC-08BO-015-01 B 1 6 UNIM UNI F 1 1–2 SD EX PAC-08BO-015-02 B 1 6 LTM LBF F 1 5.5 1.9 DA EX PAC-08BO-015-03 B 1 6 DAS IN F 1.6 0.4 DA EX PAC-08BO-015-04 B 1 6 IGU ILM F L 1 U 1.3 1.3 DA EX, RT PAC-08BO-020-01 B 1 7 LTM VER F AX 1 FU 2.1 1.5 SD EX, GN PAC-08BO-020-02 B 1 7 TAY RAD PS+MS+DS R 1 7.3 1.8 SD EX, RT PAC-08BO-022-02 B 2 6 ODO RIB POST R 1 2.6 1.2 SD EX, RT PAC-08BO-024-01 B 1 7 UNI UNI F 2 <1 PO EX PAC-08BO-025-01 B 1 7 LTM CDV F 1 2.1 DA EX, GN PAC-08BO-026-01 B 2 7 UNI UNI F 1 <1 PO EX PAC-08BO-026-02 B 2 7 UNIM LBF F 1 2.8 PAC-09BO-007/008-01 B 1 6B UNI UNI F 1 3–4 PAC-09BO-007/008-02 B 1 6B LTM LBF F 1 4.8 PAC-09BO-007/008-03 B 1 6B ODO ULN PE+PS 8.0 PAC-09BO-007-01 B 1 6B UNI UNI F 3 1–2 PAC-09BO-007-02 B 1 6B UNIM LBF F 1 2.6 0.8 PAC-09BO-007-03 B 1 6B LTM LBF F 1 4.1 PAC-09BO-007-04 B 1 6B ARM MTT 4 W R 1 FU PAC-09BO-007-05 B 1 6B JAG PH2 W L 1 PAC-09BO-007-06 B 1 6B MTM-LTM SCA PRO L 1 PAC-09BO-008-01 B 1 6B UNI UNI F 2 PAC-09BO-008-02 B 1 6B UNIM UNI F PAC-09BO-008-03 B 1 6B UNIM LBF F 1 AX R 1.0 PO EX, RT DA EX, RT 1.1 PO EX, RT 3.2 SD EX, RT, GN DA EX SD EX 1.1 PO EX, SH, STG 1.7 0.7 DA EX, RT FU 2.0 1.4 DA EX, CT FU 1.7 1.3 PO EX, GN <1 PO EX 5 1–2 PO EX 2 2–3 DA EX 1 FU 1.1 Taphonomy 205 Max length Max width Surface state 2.6 2.5 SD EX 1.4 0.9 DA EX U 1.6 1.2 PO EX U 3.2 1.5 SD EX, GN 1 2.4 0.5 SD EX, STG 1 1.6 1.0 DA EX 2.7 1.3 DA EX, CT 1.6 1.0 DA EX, RT 1 1.4 1.3 DA EX, CRK F 7 <1 PO EX UNI F 10 1–2 SD EX UNI F 15 1–2 PO EX UNIM UNI F 3 2–3 PO EX, CRK 6B UNIM LBF F 1 2.0 0.7 SD RT, BUR 1 6B UNIM LBF F 1 1.6 0.9 IT RT 1 6B STM LBF F 1 2.4 0.5 PO EX, RT B 1 6B LTM UNI F 1 3.8 1.5 PO SH, CRK PAC-09BO-010-10 B 1 6B STM-MTM SKL F 1 1.1 0.9 SD PAC-09BO-010-11 B 1 6B ODO AST PRO R 1 FU 2.7 1.5 DA EX PAC-09BO-010-12 B 1 6B ODO NVB F R 1 FU 2.2 1.2 SD EX PAC-09BO-010-13 B 1 6B MAZ CAP W L 1 FU 1.1 1.0 SD EX PAC-09BO-010-14 B 1 6B MTM-LTM MAN? F 2.9 1.3 PO EX, CRK, SH PAC-09BO-010-15 B 1 6B ODO CAL PE+PS+MS L 1 FU 5.8 2.2 SD EX, CT PAC-09BO-010-16 B 1 6B ODO MTC PE+PS L 1 FU 3.1 1.5 SD EX, CRK PAC-09BO-010-17 B 1 6B ODO AST DE R 1 FU 1.8 1.7 SD EX PAC-09BO-010-18 B 1 6B ODO RIB POST L 1 FU 2.2 1.0 SD EX PAC-09BO-010-19 B 1 6B ODO CAL DE L 1 FU 2.8 1.4 SD EX Catalogue number Plaza Unit Level ID Bone End Side Count Fusion PAC-09BO-008-04 B 1 6B ODO FEM DE PAC-09BO-008-05 B 1 6B ODO MO UP PAC-09BO-008-06 B 1 6B ARM TIB PE+PS L 1 PAC-09BO-008-07 B 1 6B ARM TIB PE+PS+MS R 1 PAC-09BO-008-08 B 1 6B ARM FIB MS+DS L PAC-09BO-008-09 B 1 6B ART MO-PM F PAC-09BO-008-10 B 1 6B MTM-LTM UNI F PAC-09BO-008-11 B 1 6B OPOV MAN DIS L 1 PAC-09BO-009-01 B 1 6B ODO MO1-2 UP R PAC-09BO-010-01 B 1 6B UNI UNI PAC-09BO-010-02 B 1 6B UNIM PAC-09BO-010-03 B 1 6B UNIM PAC-09BO-010-04 B 1 6B PAC-09BO-010-05 B 1 PAC-09BO-010-06 B PAC-09BO-010-07 B PAC-09BO-010-09 R 1 U 1 1 FU 1 Taphonomy 206 Catalogue number Plaza Unit Level ID Bone End Side Count Fusion PAC-09BO-010-20 B 1 6B ODO PH1 W PAC-09BO-010-21 B 1 6B TAY AST F PAC-09BO-010-22 B 1 6B ARM TFB PAC-09BO-010-23 B 1 6B ARM TIB PAC-09BO-010-24 B 1 6B LTM VER F PAC-09BO-018-01 B 2 6 UNIM UNI F PAC-09BO-018-02 B 2 6 UNIM UNI F PAC-09BO-018-03 B 2 6 CER ULN DS R PAC-09BO-018-04 B 2 6 ODO TIB MS R PAC-09BO-018-05 B 2 6 ART PHA DS+DE PAC-09BO-018-06 B 2 6 ODO TIB PE L 1 PAC-09BO-018-07 B 2 6 MTM ISH ACE L 1 PAC-09BO-018-08 B 2 6 UNIM UNI F PAC-09BO-019/021 B 2 6B ODO FEM PS PAC-09BO-019-01 B 2 6B MAZ ULN PS+MS PAC-09BO-019-02 B 2 6B UNI UNI F PAC-09BO-020-01 B 2 6B UNI UNI PAC-09BO-020-02 B 2 6B UNIM PAC-09BO-020-03 B 2 6B PAC-09BO-020-04 B 2 6B PAC-09BO-020-05 B 2 PAC-09BO-020-06 B PAC-09BO-020-07 PAC-09BO-020-08 Max length Max width Surface state Taphonomy 1 FU 3.9 1.4 SD EX R 1 FU 1.4 1.0 DA EX, GN DE R 1 U 2.2 0.9 PO EX, RT, CRK DS+MS L 1 2.9 1.0 DA EX, RT AX 1 1.8 1.3 DA EX 3 1–2 PO EX 1 1–2 SD EX 1 1.3 0.6 DA EX 1 3.2 1.3 SD EX, STG 1 1.5 0.9 SD FU 3.4 2.8 SD EX, GN FU 1.5 1.2 DA EX, RT PO EX, CRK 1 2–3 R 1 5.2 2.0 PO EX R 1 5.5 0.7 DA EX, GN 1 2–3 PO EX, RT F 5 <1 PO EX UNI F 5 1–2 PO EX UNIM UNI F 1 2–3 PO EX UNIM LBF F 3 2–3 PO EX, RT, STG 6B UNIM LBF F 1 2–3 SD RT, STG 2 6B TAY SCA CRA B 2 6B LTM LBF F B 2 6B LTM UNI F PAC-09BO-021-01 B 2 6B UNIM UNI PAC-09BO-021-02 B 2 6B UNIM PAC-09BO-021-03 B 2 6B MAZ R 2.2 1.4 SD EX, RT 1 5.1 1.7 PO SH, CRK 1 3.8 1.5 PO EX, RT F 2 1–2 PO EX UNI F 1 1–2 DA EX MTC PE+PS+MS+DS SD EX, GN L 1 1 FU FU 8.1 1.3 207 Max length Max width Surface state 1 2.8 0.5 SD RT F 1 1.0 0.8 DA EX, STG LBF F 1 1.9 0.7 DA EX, RT, STG LBF F 1 2.5 0.9 DA EX, RT UNI UNI F 1 <1 PO EX 6B AGO IN1 UP 1 1.2 IT RT, STG 3 6B UNIM UNI F 1 1–2 PO EX, RT 4 6 UNIM UNI F 1 <1 SD EX B 4 6 UNI UNI F 1 1–2 SD EX PAC-09BO-041-03 B 4 6 UNIM UNI F 2 1–2 PO EX, RT PAC-09BO-041-04 B 4 6 UNIM UNI F 1 2–3 PO EX, RT PAC-09BO-041-05 B 4 6 TES SHL F 1 1.5 1.4 PO EX PAC-09BO-041-06 B 4 6 TES SHL F 1 1.4 1.4 PO EX PAC-09BO-045-01 B 4 6B UNI UNI F 1 1–2 PO EX PAC-09BO-046-01 B 4 6B UNIM UNI F 1 1–2 PO EX PAC-09BO-046-02 B 4 6B MTM-LTM LBF F 1 4.0 PO EX, RT, STG PAC-09BO-047-01 B 4 6B UNI UNI F 6 <1 PO EX PAC-09BO-047-02 B 4 6B UNI UNI F 5 <1 SD PAC-09BO-047-03 B 4 6B UNIM UNI F 5 1–2 PO EX PAC-09BO-047-04 B 4 6B UNIM UNI F 3 2–3 DA EX PAC-09BO-047-05 B 4 6B UNIM UNI F 2 <1 DA EX PAC-09BO-047-06 B 4 6B ODO ULN PE+PS L 1 FU 4.1 2.0 DA EX, RT, CRK, STG PAC-09BO-047-07 B 4 6B ODO CEV CRA AX 1 FU 4.8 4.3 DA EX, RT, CRK PAC-09BO-047-08 B 4 6B ODO FEM DE L 1 FU 2.2 2.1 PO EX, GN PAC-09BO-047-09 B 4 6B UNIM UNI F 3 1–2 DA EX, RT, CRK PAC-09BO-047-10 B 4 6B UNIM UNI F 1 2–3 DA EX, RT PAC-09BO-047-13 B 4 6B ODO SES W 1 SD EX Catalogue number Plaza Unit Level ID Bone End PAC-09BO-021-04 B 2 6B AGO HUM MS+DS PAC-09BO-021-05 B 2 6B TES SHL PAC-09BO-030-01 B 3 6A UNIM PAC-09BO-030-02 B 3 6A UNIM PAC-09BO-030-03 B 3 6A PAC-09BO-031-01 B 3 PAC-09BO-032-01 B PAC-09BO-041-01 B PAC-09BO-041-02 Side Count Fusion R R FU 0.8 0.3 1.4 0.6 Taphonomy 208 Catalogue number Side Count Fusion Max length Max width Surface state 1.2 1.0 SD Plaza Unit Level ID Bone End PAC-09BO-047-14 B 4 6B ODO SES F 1 PAC-09BO-048-01 B 4 6B UNIM UNI F 1 <1 PO EX PAC-09BO-048-02 B 4 6B UNIM UNI F 6 1–2 DA EX PAC-09BO-048-03 B 4 6B UNIM UNI F 2 2–3 DA EX, RT PAC-09BO-048-04 B 4 6B LTM UNI F 1 2.5 1.8 SD EX, RT PAC-09BO-048-05 B 4 6B CAT CDV W PAC-09BO-048-06 B 4 6B ODO PH1 PE PAC-09BO-048-07 B 4 6B ODO GC W PAC-09BO-048-08 B 4 6B LTM LBF F PAC-10BO-003-01 A 1 8 UNIM UNI F PAC-10BO-008-01 A 1 6 COA TEM F 1 2.4 PAC-10BO-009-01 A 1 7 UNIM UNI F 1 1–2 PAC-10BO-009-02 A 1 7 UNIM UNI F 1 1.9 PAC-10BO-009-03 A 1 7 ODO ULN PE R 1 FU PAC-10BO-009-04 A 1 7 ODO RAD PE+PS L 1 FU PAC-10BO-009-05 A 1 7 UNIM UNI F 1 2–3 PAC-10BO-015-01 B 3 6B UNIM UNI F 1 PAC-10BO-015-02 B 3 6B UNIM UNI F PAC-10BO-015-03 B 3 6B UNI UNI PAC-10BO-016-01 B 3 6B STM-MTM LBF PAC-10BO-016-02 B 3 6B MAZ MTC PE+PS+MS R 1 PAC-10BO-016-03 B 3 6B RAB FEM DE L 1 PAC-10BO-016-04 B 3 6B MTM CN F PAC-10BO-016-05 B 3 6B GOP PM4 LO PAC-10BO-017-01 B 3 6B UNI UNI PAC-10BO-017-02 B 3 6B UNIM PAC-10BO-017-03 B 3 6B FISH AX FU Taphonomy 1 FU 1.3 0.5 PO EX, RT 1 FU 1.6 0.9 PO EX 1 FU 1.6 0.9 PO EX 1 6.0 1.9 DA EX, RT, CRK, STG 1 1–2 DA EX, RT PO EX PO EX 0.8 SD EX, BUR 6.6 3.1 PO EX, RT 4.9 3.1 DA EX, RT 1–2 PO EX 1 1–2 SD EX F 1 1–2 SD RT F 1 1.4 0.6 DA EX, RT, CRK FU 4.8 1.0 DA EX, RT, CRK, STG FU 0.8 0.8 SD EX 1 1.0 0.3 IT RT 1 1.0 0.4 DA EX, RT F 1 <1 SD EX UNI F 3 1–2 PO EX VER W-S 1 0.5 L R L AX 1.8 0.4 SD 209 Catalogue number Side Count Fusion Max length Max width Surface state Plaza Unit Level ID Bone End PAC-10BO-017-03 B 3 6B UNI UNI F 1 1–2 SD RT PAC-10BO-018-01 B 3 6B UNIM UNI F 1 <1 PO EX PAC-10BO-018-02 B 3 6B UNIM UNI F 1 1–2 PO EX PAC-10BO-019-01 B 3 6B UNIM UNI F 1 <1 PO EX PAC-10BO-019-02 B 3 6B UNIM UNI F 1 2–3 PO EX, RT PAC-10BO-021/022 B 5 6 ODO MTC PE+PS+DS PO EX, CRK, GN PAC-10BO-021-01 B 5 6 UNI UNI F 2 <1 PO EX PAC-10BO-022-01 B 5 6 UNIM UNI F 5 <1 PO EX PAC-10BO-022-02 B 5 6 UNIM UNI F 1 1–2 PO EX, RT PAC-10BO-023-01 B 5 6 UNI UNI F 4 <1 PO EX PAC-10BO-023-02 B 5 6 TES SHL F 1 PAC-10BO-023-03 B 5 6 MAZ PH1 DE+DS+MS 1 PAC-10BO-024-01 B 5 6 UNIM UNI F 1 1–2 PAC-10BO-024-02 B 5 6 PAC MO1 LO 1 1.2 PAC-10BO-025-01 B 5 6B UNIM UNI F 5 PAC-10BO-025-02 B 5 6B UNIM UNI F 2 PAC-10BO-025-03 B 5 6B UNIM UNI F 1 3–4 PAC-10BO-025-04 B 5 6B ODO NVB W PAC-10BO-025-05 B 5 6B OPOV ULN PAC-10BO-026-01 B 5 6B FISH VER PAC-10BO-026-02 B 5 6B IGU MAN+TTH Mesial PAC-10BO-026-03 B 5 6B STM LBF PAC-10BO-026-04 B 5 6B STM PAC-10BO-027-01 B 5 6B UNI PAC-10BO-027-02 B 5 6B PAC-10BO-028-01 B 5 PAC-10BO-028-02 B 5 R L 1 FU FU 7.5 1.8 Taphonomy 2.2 1.3 PO EX, CRK 1.6 0.8 SD EX PO EX SD RT, STG <1 PO EX 1–2 DA EX, RT DA EX, RT 0.7 R 1 FU 2.8 2.4 DA EX, RT, CT PE R 1 FU 1.1 0.6 SD EX, RT W-S AX 1 0.5 0.4 IT R 1 1.4 0.5 SD EX, RT F 1 0.8 0.3 SD EX LBF F 1 2.1 0.4 SD EX UNI F 1 <1 SD UNIM UNI F 1 1–2 PO EX, RT 7 UNIM UNI F 4 1–2 PO EX 7 UNIM UNI F 2 2–3 PO EX 210 Max length Max width Surface state 1 1.0 0.6 DA EX 1 1.6 0.6 DA EX, STG 1 1.3 0.5 PO EX, STG 1 3–4 PO EX, RT F 8 <1 PO EX F 6 1–2 PO EX 1 0.7 0.6 PO EX 1 1.0 0.4 SD EX F 1 <1 SD EX UNI F 1 1–2 PO EX STM UNI F 1 0.8 SD BUR UNI UNI F 7 <1 PO EX 6B UNIM UNI F 1 1–2 PO EX, RT 6 6B LTM LBF F 1 2.4 B 6 6 UNI UNI F 1 <1 PO EX B 6 6 UNIM UNI F 1 1–2 PO EX PAC-10BO-035A-01 B 6 6B PAC MO3 LO 1 1.7 SD RT PAC-10BO-035B-01 B 6 6B UNI UNI F 2 <1 DA EX PAC-10BO-035B-02 B 6 6B UNIM UNI F 6 1–2 PO EX PAC-10BO-035B-03 B 6 6B UNIM LBF F 1 2.0 0.9 PO EX PAC-10BO-035B-04 B 6 6B LTM LBF F 1 3.6 1.8 PO EX, RT PAC-10BO-035B-08 B 6 6B STM LBF F 1 1.4 0.4 PO EX, STG PAC-10BO-036A-01 B 6 6B UNI UNI F 2 <1 PO EX, STG PAC-10BO-036B-01 B 6 7 UNI UNI F 4 <1 PO EX PAC-10BO-036B-02 B 6 7 ODO LUN F R 1 1.7 0.9 SD EX PAC-10BO-036B-03 B 6 7 ODO SCP F L 1 1.6 0.8 PO EX PAC-10BO-036B-04 B 6 7 ARM SHL F 0.4 0.3 DA EX Catalogue number Plaza Unit Level ID Bone End PAC-10BO-028-03 B 5 7 ARM SHL F PAC-10BO-028-04 B 5 7 LTM RIB F PAC-10BO-028-05 B 5 7 GOP TIB PS+MS PAC-10BO-028-06 B 5 7 UNIM UNI F PAC-10BO-032-01 B 6 6 UNI UNI PAC-10BO-032-02 B 6 6 UNIM UNI PAC-10BO-032-03 B 6 6 ARM SHL F PAC-10BO-032-04 B 6 6 GOP PM4 LO PAC-10BO-033-01 B 6 6 UNI UNI PAC-10BO-033-02 B 6 6 UNIM PAC-10BO-033-03 B 6 6 PAC-10BO-034A-01 B 6 6B PAC-10BO-034A-02 B 6 PAC-10BO-034A-03 B PAC-10BO-034B-01 PAC-10BO-034B-02 Side Count Fusion R L R 1 FU 0.4 1.4 0.7 Taphonomy PO 211 Catalogue number Side Count Fusion Max length Plaza Unit Level ID Bone End PAC-10BO-038-01 B 8 6 UNI UNI F 2 <1 PAC-10BO-038-02 B 8 6 ODO PH2 F 1 2.5 PAC-10BO-040-01 PAC-11BO-001-01 B 10 6 A 1E 7 UNI UNIM UNI UNI F F 3 1 <1 2.8 UNI F 1 1–2 PAC-11BO-001-02 A 1E 7 UNIM PAC-11BO-002-01 A 1E 8 ODO PH1 DE+DS+MS 1 PAC-11BO-003-01 A 1F 7 PAC-11BO-003-02 A 1F 7 MTM-LTM UNIM LBF UNI F F 7 UNI UNI 8 UNIM PAC-11BO-003-03 PAC-11BO-004-01 A A 1F 1F FU Max width Surface state Taphonomy PO EX 1.3 PO EX PO EX 1.2 DA RT, BUR PO EX, RT 2.5 1.1 SD EX, RT, STG 1 1 2.7 1.3 1.3 0.7 PO EX, RT, BUR, DR SD RT, BUR F 1 1–2 SD RT UNI F 1 EX 1 2–3 3.7 PO W 1.3 SD EX, CRK, BUR 8.4 4.7 DA EX, RT PAC-11BO-004-02 A 1F 8 ODO PH1 PAC-11BO-004-03 A 1F 8 ODO SCA PRO PAC-96BO-064-01 B 2b 6 UNIM UNI F 1 1–2 PO EX PAC-96BO-064-02 B 2b 6 UNIM UNI F 1 2–3 PO EX, RT PAC-96BO-064-03 B 2b 6 ODO MTP DE L 1 1.9 1.7 DA EX PAC-96BO-064-04 B 2b 6 ODO HUM DS R 1 5.1 2.1 DA EX, CRK PAC-96BO-066-01 B 2+2b 5 UNIM UNI F 1 1–2 PO EX PAC-96BO-066-02 B 2+2b 6 ODO HUM DS 1 4.3 PO EX, RT PAC-96BO-067-01 B 12 7 UNI UNI F 4 <1 IT EX, RT PAC-96BO-067-02 B 12 7 UNI UNI F 1 1–2 PO EX PAC-96BO-067-03 B 12 7 ODO RIB POST L 1 3.3 0.8 DA EX, STG PAC-96BO-067-04 B 12 7 ARM TIB DE+MS+DS R 1 4.2 1.7 PO EX PAC-96BO-067-05 B 12 7 AVES LBF F 1 2.3 0.6 DA RT PAC-96BO-068-01 B 11 7 UNIM UNI F 1 1–2 PO EX PAC-96BO-068-02 B 11 7 UNIM UNI F 1 1–2 SD EX PAC-96BO-068-03 B 11 7 UNIM UNI F 1 1–2 SD EX PAC-96BO-068-04 B 11 7 MTM-LTM UNI F 1 2.5 PO EX, RT L R 1 FU U FU 1.9 1.2 212 Max length Max width Surface state 1 2.2 1.3 PO EX, RT F 1 2.1 1.6 PO EX, RT UNI F 3 <1 PO EX UNI F 3 1–2 PO EX UNIM UNI F 1 2–3 PO EX, RT MTM-LTM LBF F 1 3.5 1.1 PO EX, RT 6B OCE HUM DE 1.4 1.2 PO EX, STG 6b MTM-LTM LBF F 1 3.9 0.9 PO EX, RT 8 6B ODO MTT S 1 3.4 1.4 PO EX, RT B 1 8 UNI UNI F 4 <1 SD EX PAC-96BO-099-02 B 1 8 UNIM UNI F 4 1–2 DA EX PAC-96BO-099-03 B 1 8 UNIM UNI F 2 1–2 PO EX, RT PAC-96BO-099-05 B 1 8 UNIM UNI F 1 2–3 PO EX PAC-96BO-099-06 B 1 8 MTM-LTM LBF F 1 3.1 1.4 DA EX, RT PAC-96BO-099-07 B 1 8 MTM-LTM LBF F 5.5 0.8 DA EX, RT PAC-96BO-099-08 B 1 8 ODO MTC PE 1.5 1.4 DA EX PAC-96BO-099-09 B 1 8 ODO MTP S 1 3.6 0.7 DA EX, RT PAC-96BO-099-10 B 1 8 ODO PHA DE+DS 1 FU 1.4 1.2 SD EX PAC-96BO-099-11 B 1 8 RAB ULN PE 1 FU 1.4 0.7 SD RT, STG PAC-96BO-099-12 B 1 8 TES SHL F 1 1.0 0.5 SD EX, CRK PAC-96BO-099-13 B 1 8 TES SHL F 1 2.4 1.2 SD EX, RT, STG, CT PAC-96BO-099-14 B 1 8 MTM LBF F 1 1.6 1.4 DA EX, RT, GN, BUR PAC-96BO-100-01 B 8 8 UNIM UNI F 1 2–3 SD EX, STG PAC-96BO-100-02 B 8 8 UNIM UNI F 1 1–2 PO EX, STG PAC-96BO-103-01 B 6 7 UNI UNI F 6 <1 DA EX PAC-96BO-103-02 B 6 7 UNIM UNI F 3 1–2 DA EX PAC-96BO-103-03 B 6 7 UNIM UNI F 4 2–3 DA EX Catalogue number Plaza Unit Level ID Bone End PAC-96BO-068-05 B 11 7 MTM-LTM UNI F PAC-96BO-068-06 B 11 7 MTM-LTM LBF PAC-96BO-084-01 B 8 6B UNI PAC-96BO-084-02 B 8 6B UNIM PAC-96BO-084-03 B 8 6B PAC-96BO-084-04 B 8 6b PAC-96BO-084-05 B 8 PAC-96BO-084-05 B 8 PAC-96BO-084-06 B PAC-96BO-099-01 Side Count Fusion R 1 FU 1 L R 1 FU Taphonomy 213 Catalogue number Side Count Fusion Max length Max width Surface state Plaza Unit Level ID Bone End PAC-96BO-103-04 B 6 7 UNIM UNI F 4 1–2 DA EX PAC-96BO-103-05 B 6 7 UNIM UNI F 1 1–2 PO EX PAC-96BO-103-09 B 6 7 LTM UNI F 1 2.5 2.2 PO EX, RT PAC-96BO-103-10 B 6 7 LTM LBF F 1 2.4 1.6 PO EX, RT, CT PAC-96BO-103-11 B 6 7 ODO TRQ W L 1 FU 2.2 1.6 SD EX, STG PAC-96BO-103-12 B 6 7 ARM ULN PE+PS+MS R 1 FU 2.6 1.1 DA EX, RT, STG PAC-96BO-103-13 B 6 7 ARM CDV F AX 1 U 1.6 0.6 DA EX, RT PAC-96BO-103-14 B 6 7 ARM TIB DS+MS R 1 3.4 1.2 DA EX, RT PAC-96BO-103-15 B 6 7 ARM FIB DS+MS R 1 2.4 1.6 DA EX, RT PAC-96BO-105-01 B 8 7 UNI UNI F 1 <1 PO EX PAC-96BO-105-02 B 8 7 UNIM UNI F 2 1–2 DA EX PAC-96BO-105-03 B 8 7 FISH VER W-S 1 1.3 PO EX PAC-96BO-107-01 B 8 6B UNI UNI F 1 1–2 SD RT, BUR PAC-96BO-108-01 B 11 6B UNIM UNI F 1 1–2 PO EX PAC-96BO-108-02 B 11 6B UNIM UNI F 1 2–3 PO EX, RT PAC-96BO-108-03 B 11 6B UNIM UNI F 1 4–5 PO EX, RT PAC-96BO-108-04 B 11 6b STM-MTM LBF F 1 2.2 0.5 PO EX, RT, CRK, STG PAC-96BO-108-05 B 11 6b LTM LBF F 1 3.0 1.5 PO EX, RT PAC-96BO-108-06 B 11 6B ODO NVB F 2.9 2.5 PO EX, RT, STG PAC-96BO-109-01 B 11 6B UNIM UNI F 1 2–3 PO EX, RT PAC-96BO-109-02 B 11 6b LTM LBF F 1 3.5 PO EX, RT PAC-96BO-109-02 B 11 6B UNIM UNI F 1 <1 SD CRK PAC-96BO-109-03 B 11 6b STM-MTM LBF F 1 2.0 PO EX PAC-96BO-110-01 B 6 6 UNIM UNI F 3 <1 PO EX PAC-96BO-110-02 B 6 6 UNIM UNI F 1 1–2 PO EX PAC-96BO-110-03 B 6 6 UNIM UNI F 1 2–3 PO EX PAC-96BO-110-04 B 6 6 UNIM UNI F 1 4–5 DA EX AX L 1 FU 0.5 1.6 0.7 Taphonomy 214 Max length Max width Surface state 2.4 1.3 PO EX 1 4.6 1.8 PO EX, RT Marginal 1 1.2 1.1 PO EX F 4 <1 PO EX UNI F 2 <1 DA EX UNIM UNI F 1 1–2 SD EX 7 ARM FEM MS 7 UNIM UNI F 10 7 PAC ULN PE+PS B 10 7 UNI UNI F 1 PAC-96BO-116-01 B 3 6 UNI UNI F PAC-96BO-116-02 B 3 6 UNI UNI F PAC-96BO-117-01 B 6 6 UNIM UNI PAC-96BO-117-02 B 6 6 LTM PAC-96BO-117-03 B 6 6 PAC-96BO-118-01 B 3 6 PAC-96BO-118-02 B 3 PAC-96BO-118-03 B PAC-96BO-119-01 PAC-96BO-119-02 Catalogue number Plaza Unit Level ID Bone End PAC-96BO-110-05 B 6 6 ODO ULN PE PAC-96BO-110-06 B 6 6 LTM LBF F PAC-96BO-110-07 B 6 6 TES SHL PAC-96BO-111-01 B 8 7 UNI UNI PAC-96BO-112-01 B 8 7 UNI PAC-96BO-112-02 B 8 7 PAC-96BO-112-03 B 8 PAC-96BO-113-01 B 10 PAC-96BO-113-02 B PAC-96BO-113-03 Side Count Fusion R L 1 U PO EX, RT DA EX SD EX, RT <1 PO EX, STG 7 <1 PO EX 7 1–2 PO EX F 2 1–2 PO EX LBF F 1 3.1 1.5 PO EX, RT COL VER W 0.9 0.8 SD UNI UNI F 1 1–2 6 STM LBF F 1 1.1 3 6 MTM LBF F 1 0.9 B 4 6 UNIM UNI F 1 2–3 B 4 6 LTM LBF F 1 4.0 PAC-96BO-120-01 B 2c 6 UNIM UNI F 1 PAC-96BO-121-01 B 9 6 UNI UNI F PAC-96BO-121-02 B 9 6 UNIM UNI PAC-96BO-121-03 B 9 6 LTM LBF PAC-96BO-121-04 B 9 6 UNIM PAC-96BO-121-05 B 9 6 PAC-96BO-132-01 B 6 8 R AX 1 2.5 1 1–2 1 1 FU FU 3.5 1.4 Taphonomy 1.2 PO EX 0.5 PO SH 0.9 DA EX, RT DA EX PO EX, RT 1–2 DA EX 4 <1 DA EX F 1 1–2 DA EX, RT F 1 3.2 SD EX, STG UNI F 5 1–2 PO EX UNI UNI F 2 2–3 DA EX MTM-LTM LBF F 1 2.6 PO EX, RT 1.4 1.6 1.4 215 Catalogue number Side Count Fusion Max length Max width Surface state Plaza Unit Level ID Bone End PAC-96BO-142-01 B 1 6 UNI UNI F 2 <1 DA EX PAC-96BO-142-02 B 1 6 UNIM UNI F 1 1–2 DA EX PAC-96BO-142-03 B 1 6 TES SHL F 3 0.8 0.7 PO EX PAC-96BO-142-04 B 1 6 AVES STX F AX 1 1.0 0.5 PO EX PAC-96BO-142-05 B 1 6 GOP TIB PE+PS L 1 0.8 0.7 PO EX PAC-96BO-143-01 B 2c 6 UNIM UNI F PO EX PAC-96BO-143-02 B 2c 6 TAY PM3 UP PAC-96BO-148-01 B 5 7 ARM TIB DS+MS PAC-96BO-149-01 B 5 7 UNIM UNI PAC-96BO-151-01 B 6 7 UNIM UNI PAC-96BO-158-01 B 8 6 UNI UNI F PAC-96BO-158-02 B 8 6 CAN CN UP PAC-96BO-160-01 B 10 6 TAY PH2 W 1 PAC-96BO-161-01 B 10 7 STM-MTM LBF F PAC-96BO-162-01 B 11 6B ODO ILM F PAC-96BO-163-01 B 11 7 UNI UNI F PAC-96BO-163-02 B 11 7 UNIM UNI PAC-96BO-163-03 B 11 7 UNIM PAC-96BO-163-04 B 11 7 PAC-96BO-163-05 B 11 7 PAC-96BO-163-06 B 11 PAC-96BO-163-08 B PAC-96BO-163-09 PAC-96BO-163-10 U Taphonomy 1 3–4 L 1 1.0 0.9 DA EX R 1 2.5 1.1 PO EX, RT, STG F 1 1–2 PO EX, RT F 2 2–3 DA EX 2 <1 DA EX 1 1.5 0.5 DA EX, RT 1.8 1.0 SD EX, RT 1 1.5 0.7 DA EX, RT, CRK, GN 1 3.8 1.5 PO EX, STG 5 <1 PO EX F 2 2–3 PO EX, RT UNI F 2 2–3 PO EX, RT UNIM UNI F 4 1–2 DA EX UNIM UNI F 4 2–3 DA EX 7 UNIM UNI F 2 2–3 SD EX 11 7 STM LBF F 1 1.5 0.4 DA EX, STG B 11 7 LTM LBF F 1 3.6 0.9 SD RT B 11 7 LTM LBF F 1 3.7 1.4 DA EX, RT PAC-96BO-163-11 B 11 7 LTM LBF F 1 3.9 1.4 PO EX, RT PAC-96BO-163-12 B 11 7 LTM LBF F 1 5.5 1.6 SD EX, RT PAC-96BO-163-13 B 11 7 ARM SHL F 1 1.4 0.5 SD EX L L FU 216 Max length Max width Surface state 1.1 0.9 DA EX, RT 1 4.7 1.6 DA EX, RT, STG 1 1.8 1.1 PO EX 1 1.7 0.5 SD RT, STG 1 1.4 0.5 DA EX, RT 1.2 1.0 DA EX DA EX DA EX, RT, GN <1 PO EX 4 1–2 PO EX F 1 1–2 PO SH, CRK F 1 4.1 1.9 DA EX, RT UNI F 1 2.2 1.2 SD RT, BUR UNI UNI F 1 <1 PO EX 6 SER CDV W-S 6 TAY PH1 PE+PS 1 97-SU4 6 MTM UNI F B 97-RU1 6C UNIM UNI PAC-97BO-027-01 B 97-SU3 6 UNIM PAC-97BO-029-01 B 97-U1 6 UNI PAC-97BO-029-02 B 97-U1 6 PAC-97BO-029-03 B 97-U1 6 PAC-97BO-029-04 B 97-U1 6 PAC-97BO-031-01 B 97-U3 6 PAC-97BO-031-02 B 97-U3 6 PAC-97BO-031-03 B 97-U3 PAC-97BO-052-01 B 97-U1 Catalogue number Plaza Unit Level ID Bone End Side Count Fusion PAC-96BO-163-14 B 11 7 MAZ MAL W L 1 PAC-96BO-163-15 B 11 7 ODO TIB MS R PAC-96BO-163-16 B 11 7 ODO PH3 PE+PS PAC-96BO-163-17 B 11 7 ICT DRS ANT AX PAC-96BO-163-18 B 11 7 FISH DRS ANT AX PAC-96BO-163-20 B 11 7 ODO SES W 1 PAC-96BO-164-01 B 11 7B UNIM UNI F 2 1–2 PAC-96BO-164-02 B 11 7B TES SHL F 1 1.2 PAC-97BO-007-01 B 97-SU1 6 UNIM UNI F 1 PAC-97BO-007-02 B 97-SU1 6 UNIM UNI F PAC-97BO-007-03 B 97-SU1 6 UNIM UNI PAC-97BO-011-01 D 97D1 7 UNIM LBF PAC-97BO-011-02 D 97D1 7 UNIM PAC-97BO-016-01 B 97-U1 6 PAC-97BO-016-02 B 97-U1 PAC-97BO-016-03 B 97-U1 PAC-97BO-021-01 B PAC-97BO-025-01 AX FU FU 1.0 0.7 DA EX 0.7 0.5 PO EX 1 1.3 0.4 PO BUR F 1 <1 SD EX LBF F 1 1.8 SD EX UNI F 1 <1 PO EX UNIM UNI F 1 1–2 PO EX ODO RIB F R 1 2.0 0.7 DA EX, CT ODO MO LO L 1 1.2 0.5 PO EX UNIM UNI F 1 <1 PO EX UNIM UNI F 3 1–2 PO EX 6 MAZ LUN W PO EX 8 UNI UNI F DA EX L 1 0.8 Taphonomy 1 3 FU FU 1.3 <1 0.6 1.0 217 Catalogue number Plaza Unit Level ID Bone End PAC-97BO-052-02 B 97-U1 8 UNIM UNI F PAC-97BO-052-03 B 97-U1 8 ODO CAL DE+MS Side Count Fusion 1 R 1 Max length Max width 2–3 FU 4.3 1.6 Surface state Taphonomy DA EX DA EX 218 Table A.2 Pacbitun dataset for the late Middle Preclassic period Catalogue number Side Surface Taphonomy state Level ID Bone End P95-00-02 B 1 5 UNIM UNI F 2 1–2 SD EX, CRK P95-00-03 B 1 5 UNIM UNI F 3 2–3 DA EX P95-00-04 B 1 5 UNIM UNI F 1 3–4 PO EX, RT P95-00-05 B 1 5 UNIM UNI F 1 1.1 0.7 IT BUR P95-00-06 B 1 5 LTM LBF F 1 2.9 1.4 PO EX, RT P95-00-07 B 1 5 LTM LBF F 1 3.7 1.0 PO EX, RT P95-00-08 B 1 5 LTM LBF F 1 5.6 1.2 PO EX, RT, STG, PN P95-02-01 B 1 4 LTM LBF F 1 6.3 1.9 PO EX P95-03-01 B 1 3 UNIM UNI F 1 1.2 PO EX P95-04-01 B 1 5 UNIM UNI F 1 1.2 PO EX P95-05-01 B 1 5 UNIM UNI F 1 2.2 PO EX P95-06-01 B 1 4 UNI UNI F 4 <1 PO EX P95-06-02 B 1 4 UNI UNI F 1 1–2 PO EX P95-06-03 B 1 4 UNI UNI F 2 2–3 PO EX P95-06-04 B 1 4 LTM LBF F 1 6.0 2.1 DA EX, RT, SH, STG P95-06-05 B 1 4 IGU VER F AX 1 1.0 0.9 DA EX, RT, STG P95-07-01 B 1 3 ODO CEV CAU AX 1 2.6 2.2 DA EX, RT P95-07-02 B 1 3 UNIM UNI F 1 1.0 PO EX P95-07-03 B 1 3 LTM LBF F 1 3.8 PO EX, RT, STG P95-08-01 B 1 5 UNI UNI F 1 1–2 PO EX P95-09-01 B 1 3 UNIM UNI F 5 <1 PO EX P95-09-02 B 1 3 UNIM UNI F 13 1–2 PO EX, STG P95-09-03 B 1 3 UNIM LBF F 3 1–2 PO EX P95-09-04 B 1 3 UNIM LBF F 4 2–3 PO EX P95-09-05 B 1 3 ODO AST PRO PO EX, STG, CRK 1 Fusion Max width Unit L Count Max length Plaza FU 3.0 1.0 2.2 219 Plaza Unit Level ID Bone End Side Count Fusion Max length Max width P95-09-06 B 1 3 ODO HUM DE R 1 FU 3.8 1.5 PO EX, CRK P95-09-07 B 1 3 MAR NAV W R 1 FU 1.0 0.8 PO EX P95-09-08 B 1 3 COL VER W AX 1 FU 1.0 1.0 PO EX P95-09-09 B 1 3 COL VER W AX 1 FU 1.0 1.0 PO EX P95-09-10 B 1 3 LTM UNI F 1 3.6 1.2 PO EX P95-09-11 B 1 3 LTM LBF F 1 2.8 1.4 PO EX, RT P95-09-12 P95-09-14 B 1 3 MTM 3 AVES F DS 1 1 2.6 2.4 0.9 0.7 STG 1 LBF TBT PO B SD RT, STG P95-09-14 B 1 3 LTM LBF F 1 4.7 1.3 PO EX, RT, CRK P95-11-01 B 1 4 UNIM UNI F 6 <1 PO EX P95-11-02 B 1 4 ODO NVB W R 1 P95-11-03 B 1 4 ODO HUM DE+DS R 1 P95-11-04 B 1 4 ODO GC F R 1 P95-12-01 B 1 3 UNIM UNI F 1 2.0 P95-12-02 B 1 3 ARM SHL F 1 0.8 P95-13-01 B 1 3 UNIM UNI F 1 1.6 PO EX P95-14-01 B 1 ext. 3 UNIM UNI F 1 1.4 PO EX P95-15-01 B 1 3 UNIM UNI F 1 1–2 PO EX P95-15-02 B 1 3 ARM CAL F DA EX P95-16-01 B 1 3 UNI UNI F 4 <1 PO EX P95-16-02 B 1 3 UNIM UNI F 1 1.7 PO EX P95-16-04 B 1 3 LTM LBF F 1 7.9 PO EX, STG P95-17-01 B 1 5 UNIM UNI F 2 1–2 DA EX P95-17-02 B 1 5 UNIM LBF F 1 1.7 DA EX, BUR P95-18-01 B 1 3 UNI UNI F 3 1–2 PO EX P95-18-02 B 1 3 UNI UNI F 1 2.8 1.3 PO EX P95-18-03 B 1 3 LTM UNI F 1 1.9 1.6 PO EX Catalogue number R L 1 FU FU FU Surface Taphonomy state 2.7 2.4 DA RX, RT, STG 5.7 2.3 DA EX 1.7 0.8 SD EX, STG DA EX 1.9 0.6 0.8 1.9 IT 220 Max length Max width 1 2.2 1.4 DA EX 1 3.7 1.6 PO EX <1 PO EX 1–2 PO EX, CRK 2–3 PO EX 2 3–4 PO EX F 1 3–4 PO EX F 1 4–5 PO EX UNI F 2 1–2 PO EX UNIM UNI F 1 2–3 PO EX 3 UNI UNI F 2 1–2 PO EX 3 UNIM UNI F 9 1–2 PO EX, STG 1 3 UNIM LBF F 2 2–3 PO EX, RT B 1 3 UNIM UNI F 1 1–2 PO EX, GN P95-21-04 B 1 3 ARM FEM PE P95-21-05 B 1 3 TAY PH1 W P95-21-06 B 1 3 ODO CAL DE+DS P95-21-07 B 1 3 MTM-LTM LBF F 1 P95-21-09 B 1 3 ODO SES W 1 P95-22-01 B 1 3 UNIM UNI F 7 <1 P95-22-02 B 1 3 UNIM UNI F 10 1–2 P95-22-03 B 1 3 STM LBF F 1 2.0 P95-22-04 B 1 3 STM LBF F 1 P95-22-05 B 1 3 DOG MO1 LO L 1 P95-22-06 B 1 3 MAZ MAL W L 1 P95-22-07 B 1 3 ODO MO3 LO R P95-22-08 B 1 3 MTM-LTM LBF F Catalogue number Plaza Unit Level ID Bone End Side Count P95-18-04 B 1 3 ODO TIB PE L P95-18-05 B 1 3 ODO ILM F R P95-19-01 B UNIM UNI F 1 P95-19-02 B UNIM UNI F 1 P95-19-03 B UNIM UNI F 1 P95-19-04 B UNIM UNI F P95-19-05 B UNIM LBF P95-19-06 B UNIM UNI P95-20-01 B 1 3 UNIM P95-20-02 B 1 3 P95-20-04 B 1 P95-21-01 B 1 P95-21-02 B P95-21-03 L R Fusion Surface Taphonomy state 1 FU 1.0 0.9 PO EX, GN 1 FU 1.3 0.6 PO EX 1 FU 3.4 1.9 PO EX 3.3 0.9 PO EX, RT, BUR 0.9 0.9 PO EX PO EX PO EX 0.4 PO EX, RT 1.5 0.4 PO EX, RT 2.2 2.2 PO EX, CRK, STG 0.9 0.8 PO EX, RT 1 2.2 0.9 DA EX 1 2.0 0.9 PO EX FU FU 221 Catalogue number Side Fusion Max width Surface Taphonomy state Unit Level ID Bone End P95-23-01 B 1 3 UNIM UNI F 6 <1 PO EX P95-23-02 B 1 3 UNIM UNI F 2 1–2 PO EX P95-23-03 B 1 3 UNIM UNI F 2 2–3 PO EX P95-23-04 B 1 3 UNIM UNI F 1 1.9 0.9 SD BUR P95-23-05 B 1 3 CER TRV F AX 1 1.1 1.0 PO EX P95-23-06 B 1 3 LTM VER F AX 1 2.0 1.7 DA EX P95-24-01 B 1 3 UNIM UNI F 2 1–2 PO EX P95-24-02 B 1 3 UNIM UNI F 3 2–3 PO EX P95-24-03 B 1 3 MTM LBF F 1 2.6 0.9 PO EX, PN P95-24-04 B 1 3 MTM LBF F 1 2.0 1.1 PO EX, RT P95-25-01 B 1 4 UNIM UNI F 16 <1 PO EX P95-25-02 B 1 4 UNIM UNI F 7 1–2 PO EX P95-25-03 B 1 4 UNIM UNI F 3 1–2 PO EX P95-25-04 B 1 4 MTM-LTM LBF F 1 3.4 1.0 PO EX, BUR P95-25-06 B 1 4 TAY RUL PE+PS P95-25-07 B 1 4 MAZ PH1 DE+DS+MS P95-25-08 B 1 4 ARM CAL PE+PS P95-26-01 B UNIM UNI F 6 P95-26-02 B UNIM UNI F P95-26-03 B UNIM UNI F P95-26-04 B UNIM UNI P95-26-05 B UNIM UNI P95-26-06 B ARM SHL F P95-26-06 B ODO FEM PS P95-26-07 B TES SHL P95-27-01 B UNIM P95-27-02 B UNIM R Count Max length Plaza 1 FU 5.2 2.0 DA EX, RT, CRK 1 FU 2.5 0.9 PO EX, RT 1 FU 1.4 1.1 DA EX <1 PO EX 6 1–2 PO EX, STG 7 1–2 PO EX F 2 2–3 PO EX F 3 2–3 SD RT, BUR 1 0.9 0.5 DA EX, STG 1 4.7 1.3 PO EX F 1 2.1 1.5 PO EX UNI F 1 2–3 PO EX UNI F 1 3–4 PO EX R L 222 Catalogue number Fusion Surface Taphonomy state Level ID Bone End P95-28-01 B 1 4 UNIM UNI F 1 1–2 DA EX P95-29-01 B 1 3+4 UNIM UNI F 1 2–3 SD STG P95-29-02 B 1 3+4 UNIM UNI F PO EX P95-30-01 B BUF HUM W L 1 P95-30-03 B ODO DP4 LO R P95-30-04 B UNIM UNI F P95-30-05 B TES HUM F P95-32-01 B UNIM UNI F P95-32-02 B MAZ TIB PS+MS P95-32-03 B ARM RAD PE+PS+MS P95-33-01 B 1 4 UNIM UNI F 8 P95-33-02 B 1 4 UNIM UNI F 3 P95-33-03 B 1 4 UNIM UNI F 4 1–2 P95-33-04 B 1 4 MTM-LTM SKL F 1 2.4 P95-33-05 B 1 4 UNIM LBF F 1 1.2 P95-33-06 B 1 4 UNIM UNI F 1 4–5 P95-33-07 B 1 4 ODO PH3 W 1 P95-33-09 B 1 4 TAP PM3 LO L 1 P95-33-10 B 1 4 GOP IN1 UP R 1 P95-33-11 B 1 4 MTM PH3 W P95-33-12 B 1 4 IGU ULN DE+DS+MS P95-34-01 B UNIM UNI F 1 P95-34-02 B MAZ PH1 DE+DS+MS 1 P95-41-01 B 1 4 UNI UNI F 1 1–2 P95-75-01 B 1 3 UNIM LBF F 1 1.1 P95-90-01 B CER MTT PS 1 PAC-08BO-001-01 B UNIM LBF F 1 4 Count Max width Unit 1 Side Max length Plaza 1 L 1–2 1.8 0.5 IT 1 1.1 1.1 SD EX 1 1–2 DA EX, RT, BUR IT RT, STG 1 FU FU 1.5 0.6 3 1–2 L 1 8.8 2.9 SD EX, RT, STG, GN R 1 1.8 0.5 SD EX <1 PO EX 1–2 PO EX PO EX 1.5 PO EX, RT 0.7 DA EX, BUR PO EX, STG R R FU FU SD 3.0 1.3 SD EX 1.8 1.5 PO EX, STG 1.8 1.4 SD EX, RT 1 FU 1.6 0.7 DA EX 1 FU 1.8 0.3 SD EX PO EX PO EX, GN PO EX 0.6 SD BUR 3.3 0.8 PO EX, STG 2.1 1.9 PO EX 1–2 FU 1.9 0.9 223 Catalogue number Plaza Unit Level ID Bone End PAC-08BO-002-01 B 1 4 UNI UNI F PAC-08BO-003-01 B 1 4 ARM TIB DS PAC-08BO-004-01 B 1 4 UNIM UNI PAC-08BO-005-01 B 1 4 UNIM UNI PAC-08BO-005-02 B 1 4 UNIM PAC-08BO-006-01 B 1 5 UNIM PAC-08BO-006-02 B 1 5 PAC-08BO-006-03 B 1 5 PAC-08BO-006-04 B 1 PAC-08BO-007-01 B PAC-08BO-007-02 PAC-08BO-008-01 Side Count Fusion Max length 1 1–2 1 2.2 F 1 F 3 UNI F UNI F UNIM UNI F ODO TRV F L 5 LTM VER F AX 1 1 5 UNIM UNI F 1 B 1 5 UNIM UNI F B 1 5 UNIM UNI F PAC-08BO-009-01 B 1 5 UNIM UNI PAC-08BO-009-02 B 1 5 UNIM PAC-08BO-009-03 B 1 5 PAC-08BO-010-02 B 1 5 PAC-08BO-010-03 B 1 5 PAC-08BO-011-01 B 1 5 PAC-08BO-011-02 B 1 PAC-08BO-012-01 B 1 PAC-08BO-012-02 B PAC-08BO-013-01 Max width Surface Taphonomy state PO EX PO EX, RT, STG 1–2 PO EX <1 PO EX 1 1–2 SD EX 1 <1 PO EX 2 1–2 PO EX 1 1.6 1.4 PO EX, STG, CRK 1.7 1.6 PO EX, RT <1 PO EX 1 2–3 DA EX 5 <1 PO EX F 2 <1 PO EX UNI F 1 1–2 PO EX VIP VER F UNIM UNI F FISH VER W-S UNIM UNI 5 ODO 5 UNIM 1 5 B 1 PAC-08BO-013-02 B PAC-08BO-013-03 B PAC-08BO-016-01 R AX 1 U FU 0.7 0.8 PO EX DA EX SD EX SD EX, RT, STG DA SH, CRK PO EX 1–2 DA EX, STG 1 1–2 PO EX F 1 1–2 PO EX F 1 1.9 PO EX, RT UNI F 10 <1 PO EX UNIM UNI F 4 1–2 PO EX VIP VER F PO EX 2 1–2 1 0.6 F 1 4–5 MTP S 1 3.6 UNI F 1 1–2 UNIM UNI F 1 5 UNIM UNI F 1 5 UNIM UNI 1 5 STM LBF B 2 4 UNIM PAC-08BO-016-02 B 2 4 PAC-08BO-016-03 B 2 4 AX AX 1 FU 1.8 0.3 0.5 1.2 0.5 0.8 224 Catalogue number Side Count Fusion Max length Max width Surface Taphonomy state Plaza Unit Level ID Bone End PAC-08BO-017-01 B 2 4 UNIM UNI F 1 2–3 SD STG PAC-08BO-018-01 B 2 5 UNIM UNI F 1 <1 PO EX PAC-08BO-018-02 B 2 5 UNIM UNI F 2 1–2 PO EX PAC-08BO-018-03 B 2 5 UNIM UNI F 2 2–3 PO EX, RT PAC-08BO-019-01 B 2 5 UNIM UNI F 3 <1 PO EX PAC-08BO-019-02 B 2 5 UNIM UNI F 2 1–2 PO EX PAC-08BO-021-01 B 1 4 UNIM UNI F 1 2–3 SD EX PAC-08BO-023-01 B 2 5 UNI UNI F 1 1–2 SD PAC-08BO-023-02 B 2 5 AVES LBF F 1 2.1 PAC-09BO-001-01 B 1 4 UNIM UNI F 6 PAC-09BO-001-02 B 1 4 UNIM UNI F PAC-09BO-001-03 B 1 4 UNIM UNI F PAC-09BO-001-04 B 1 4 UNIM UNI PAC-09BO-002-01 B 1 5 UNI PAC-09BO-002-02 B 1 5 PAC-09BO-002-03 B 1 5 PAC-09BO-002-04 B 1 PAC-09BO-002-05 B PAC-09BO-002-06 PAC-09BO-003-01 DA EX, RT <1 PO EX 2 1–2 PO EX 2 2–3 PO EX, RT F 1 1–2 PO EX, CRK UNI F 1 <1 PO EX UNIM LBF F 1 1.7 PO EX, RT UNIM UNI F 1 2–3 PO EX, RT 5 ODO NVB F 1 5 STM LBF F B 1 5 CER MTP B 1 5 UNI UNI PAC-09BO-003-02 B 1 5 UNIM PAC-09BO-003-03 B 1 5 PAC-09BO-003-06 B 1 PAC-09BO-003-07 B 1 PAC-09BO-003-08 B PAC-09BO-003-09 PAC-09BO-003-10 L 1 FU 0.5 0.6 1.4 1.0 PO EX 1 1.5 0.4 PO EX, RT S 1 3.8 1.3 PO EX, STG, PN F 4 <1 PO EX UNI F 10 1–2 PO EX UNIM UNI F 3 2–3 PO EX 5 UNIM LBF F 1 1.6 1.3 DA EX, RT, BUR 5 ODO PH1 DE+DS+MS+PS 1 FU 3.6 1.3 PO EX 1 5 ODO PH1 DE 1 FU 1.2 1.0 PO EX, CRK B 1 5 ODO PH2 DE 1 FU 1.8 1.4 SD EX, BUR B 1 5 ODO PH2 PE+PS 1 FU 1.9 1.4 SD EX, BUR 225 Plaza Unit Level ID Bone End Side Count Fusion Max length Max width PAC-09BO-003-11 B 1 5 PUM HUM DE L 1 FU 5.2 4.9 PO EX, RT PAC-09BO-003-12 B 1 5 ODO HUM DS R 1 2.8 1.6 DA EX, STG PAC-09BO-003-13 B 1 5 GOP IN1 LO 1 1.8 0.4 SD EX, RT PAC-09BO-003-14 B 1 5 STM LBF F 1 1.1 0.4 PO EX, RT, STG PAC-09BO-003-15 B 1 5 MTM-LTM LBF F 1 4.7 1.1 DA EX, RT PAC-09BO-004-01 B 1 5 UNI UNI F 1 1–2 PO EX, STG, CRK PAC-09BO-005-01 B 1 5 UNI UNI F 19 <1 PO EX PAC-09BO-005-02 B 1 5 UNIM UNI F 7 1–2 PO EX PAC-09BO-005-03 B 1 5 UNIM UNI F 1 3–4 PO EX, RT PAC-09BO-005-04 B 1 5 UNIM UNI F 1 3–4 DA EX, RT PAC-09BO-005-05 B 1 5 CER TRV CEN AX 1 FU 1.6 1.0 PO EX PAC-09BO-005-06 B 1 5 LTM LMV F AX 1 FU 3.3 2.1 DA EX PAC-09BO-005-07 B 1 5 LTM LMV F AX 1 FU 2.2 1.2 DA EX PAC-09BO-005-08 B 1 5 MTM-LTM VER CEN AX 1 FU 1.1 0.7 SD RT PAC-09BO-005-11 B 1 5 LTM VER CEN AX 1 FU 1.8 1.1 DA EX, GN PAC-09BO-006-01 B 1 5 UNI UNI F 1 <1 DA EX PAC-09BO-006-02 B 1 5 STM LBF F 1 1.2 PO EX PAC-09BO-011-01 B 2 4 UNIM UNI F 1 1–2 PO EX, RT PAC-09BO-012-01 B 2 5 UNIM UNI F 1 <1 PO EX, RT PAC-09BO-013-01 B 2 5 UNIM UNI F 1 <1 PO EX PAC-09BO-013-02 B 2 5 ODO MTP DE 1 DA EX, GN PAC-09BO-014-01 B 2 5 UNI UNI F 6 <1 PO EX PAC-09BO-014-02 B 2 5 UNIM UNI F 3 1–2 PO EX PAC-09BO-014-03 B 2 5 UNI UNI F 1 1–2 DA EX PAC-09BO-014-04 B 2 5 UNIM LBF F 1 2.2 1.2 DA EX, RT PAC-09BO-014-05 B 2 5 ODO PUB ACE 2.2 1.9 PO EX PAC-09BO-014-06 B 2 5 LTM LBF F 5.0 1.6 PO EX, CRK, STG Catalogue number L 1 1 U FU 2.0 0.3 1.8 Surface Taphonomy state 226 Catalogue number Plaza Unit Level ID Bone End Side Count PAC-09BO-015-01 B 2 5 UNIM UNI F 3 PAC-09BO-015-03 B 2 5 ODO SES W 1 PAC-09BO-016-01 B 2 5 UNI UNI F 1 PAC-09BO-016-02 B 2 5 UNIM UNI F 7 PAC-09BO-016-04 B 2 5 UNIM UNI F 4 PAC-09BO-016-05 B 2 5 UNIM LBF F PAC-09BO-016-06 B 2 5 UNIM UNI F PAC-09BO-016-07 B 2 5 ODO RAD PS R PAC-09BO-016-08 B 2 5 ODO CAP W R 1 PAC-09BO-016-09 B 2 5 MAZ PH3 W PAC-09BO-016-10 B 2 5 ODO MTP PAC-09BO-016-11 B 2 5 ODO PH3 PAC-09BO-016-12 B 2 5 AGO MTT 4 PE+PS+MS PAC-09BO-016-13 B 2 5 TES SHL F PAC-09BO-016-14 B 2 5 LTM UNI PAC-09BO-016-15 B 2 5 LTM UNI PAC-09BO-017-01 B 2 5 UNIM PAC-09BO-022-01 B 3 4 PAC-09BO-022-02 B 3 PAC-09BO-023-01 B 3 PAC-09BO-024-01 B PAC-09BO-024-02 Fusion Max length Max width PO EX SD EX <1 PO EX 1–2 PO EX 1–2 DA EX, RT 1 2–3 DA EX, RT 2 2–3 DA EX, STG 1 2.9 1.0 DA EX, STG FU 1.7 1.3 PO EX, GN 1 FU 1.8 1.0 DA EX DE 1 FU 1.2 1.2 PO EX W 1 FU 2.4 1.5 PO EX 1 FU 2.0 0.5 PO EX 1 1.1 1.1 PO SH F 1 3.9 0.9 DA EX, RT F 1 2.6 1.8 PO EX LBF F 1 3.2 1.4 PO EX, RT UNIM UNI F 5 1–2 PO EX, RT 4 UNIM LBF F 1 1.4 PO EX, RT, BUR 5 UNI UNI F 1 <1 PO EX, RT 3 5 UNI UNI F 10 <1 PO EX B 3 5 UNIM UNI F 22 1–2 PO EX PAC-09BO-024-03 B 3 5 UNIM UNI F 7 2–3 PO EX, RT PAC-09BO-024-06 B 3 5 UNIM UNI F 5 1–2 PO EX PAC-09BO-024-07 B 3 5 ODO PH1 DE+DS+MS+PS 1 FU 3.5 1.1 PO EX, GN PAC-09BO-024-08 B 3 5 ODO HUM DE 1 FU 2.9 2.7 PO EX PAC-09BO-024-09 B 3 5 ODO PH1 PE 1.8 0.7 DA EX R L 1 1–2 Surface Taphonomy state FU 1.0 1.0 1.2 227 Max length Max width 1 1.8 0.9 PO EX F 1 4.6 1.3 PO EX UNI F 1 2.7 1.7 PO EX UNI F 1 3.2 1.9 PO EX UNIM UNI F 4 1–2 PO EX, RT 4 UNI UNI F 6 <1 PO EX 1 4 UNIM UNI F 1 1–2 PO EX, RT 1 4 UNIM UNI F 1 1–2 PO EX, RT B 1 4 UNIM UNI F 1 2–3 DA EX, RT PAC-09BO-028-01 B 1 4 UNI UNI F 1 1–2 PO EX PAC-09BO-029-01 B 3 5 UNIM UNI F 1 1–2 PO EX, RT PAC-09BO-033-01 B 4 4 UNIM UNI F 1 <1 PO EX PAC-09BO-033-02 B 4 4 UNIM UNI F 3 2–3 PO EX, RT PAC-09BO-033-04 B 4 4 ODO CAL DE+DS PO EX, SH, CRK PAC-09BO-034-01 B 4 4 UNI UNI F 2 <1 PO EX, RT PAC-09BO-034-02 B 4 4 UNIM UNI F 3 1–2 PO EX, RT PAC-09BO-034-03 B 4 4 UNIM UNI F 2 1–2 SD EX PAC-09BO-034-04 B 4 4 UNIM UNI F 1 1–2 PO EX, CRK, BUR PAC-09BO-034-05 B 4 4 UNIM LBF F 1 2.6 1.1 PO EX, RT PAC-09BO-034-06 B 4 4 STM-MTM LBF F 1 1.2 0.7 DA CRK, BUR PAC-09BO-034-07 B 4 4 MTM-LTM MO-PM F 1 1.5 0.6 PO EX, RT PAC-09BO-035-01 B 4 4 UNI UNI F 4 <1 PO EX PAC-09BO-035-02 B 4 4 UNIM UNI F 4 1–2 PO EX, RT PAC-09BO-035-03 B 4 4 UNIM UNI F 1 3–4 PO EX, RT PAC-09BO-036-01 B 4 4 ODO MO UP 1 1.1 SD EX, BUR PAC-09BO-037-01 B 4 4 UNIM UNI F 11 <1 PO EX PAC-09BO-037-02 B 4 4 UNIM UNI F 2 1–2 PO EX Catalogue number Plaza Unit Level ID Bone End Side Count PAC-09BO-024-10 B 3 5 ODO PM3-4 UP R PAC-09BO-024-11 B 3 5 LTM LBF PAC-09BO-024-12 B 3 5 LTM PAC-09BO-024-13 B 3 5 LTM PAC-09BO-025-01 B 1 4 PAC-09BO-026-01 B 1 PAC-09BO-026-02 B PAC-09BO-026-03 B PAC-09BO-027-01 L L 1 Fusion FU 2.9 1.7 0.6 Surface Taphonomy state 228 Catalogue number Plaza Unit Level ID Bone End PAC-09BO-037-04 B 4 4 UNIM UNI F PAC-09BO-037-05 B 4 4 ODO RAD PE PAC-09BO-037-06 B 4 4 MTM VER F PAC-09BO-038-01 B 4 5 UNIM UNI F PAC-09BO-039-01 B 4 5 UNIM UNI PAC-09BO-039-02 B 4 5 MTM-LTM PAC-09BO-039-03 B 4 5 PAC-09BO-040-01 B 4 5 PAC-09BO-040-02 B 4 PAC-09BO-040-03 B PAC-09BO-040-04 PAC-09BO-040-06 Side Count Fusion 2 R Max width 2–3 PO EX, RT 1.0 SD EX 1 1.5 0.7 PO EX, RT 1 1–2 PO EX F 3 1–2 PO EX LBF F 1 3.0 1.3 PO EX, RT ODO MTT PE 2.1 1.5 DA EX UNI UNI F 3 <1 PO EX 5 UNIM UNI F 9 1–2 PO EX 4 5 UNIM UNI F 3 2–3 PO EX B 4 5 UNIM LBF F B 4 5 ODO GC F R 1 PAC-09BO-040-07 B 4 5 ODO RAD DE R PAC-09BO-040-08 B 4 5 MTM-LTM LBF PAC-09BO-042-01 B 4 5 UNIM PAC-09BO-043-01 B 5 4 UNIM PAC-09BO-044-01 B 5 4 PAC-09BO-049-01 B 5 PAC-09BO-050-01 B PAC-09BO-050-02 B PAC-09BO-051-01 1 FU Surface Taphonomy state 1.4 L 1 Max length FU 1 2.6 1.3 DA EX 1.4 0.9 PO EX 1 4.0 1.1 PO EX, RT F 1 5.1 1.2 PO EX, RT LBF F 1 2.7 1.1 PO EX UNI F 1 1–2 PO EX UNIM UNI F 1 1–2 PO EX 4 UNIM UNI F 1 1–2 SD EX 5 4 UNIM UNI F 1 1–2 PO EX 5 4 UNIM UNI F 1 1–2 PO EX B 6 4 UNIM UNI F 1 1–2 PO EX, RT PAC-09BO-052-01 B 6 4 LTM LBF F 1 2.9 1.6 PO EX, RT PAC-09BO-053-01 B 7 4 MTM-LTM TTH F 1 1.3 0.7 PO RT PAC-09BO-054-01 B 8 4 UNIM UNI F 1 <1 PO EX PAC-09BO-054-02 B 8 4 UNIM UNI F 3 1–2 PO EX PAC-09BO-054-03 B 8 4 UNIM UNI F 1 2–3 PO EX PAC-09BO-054-04 B 8 4 UNIM UNI F 1 1–2 PO EX FU 229 Catalogue number Side Surface Taphonomy state Level ID Bone End PAC-09BO-055-01 B 10 4 UNIM UNI F 4 <1 PO EX PAC-09BO-055-02 B 10 4 UNIM UNI F 4 1–2 PO EX PAC-09BO-056-01 B 2 4 UNI UNI F 5 <1 PO EX PAC-09BO-056-02 B 2 4 UNIM UNI F 13 1–2 PO EX PAC-09BO-056-03 B 2 4 UNIM UNI F 5 1–2 DA EX PAC-09BO-056-04 B 2 4 UNIM UNI F 2 2–3 PO EX, RT PAC-09BO-056-05 B 2 4 UNIM LBF F 1 1.3 1.2 SD EX, RT, BUR PAC-09BO-056-08 B 2 4 MTM-LTM RIB F 1 3.8 0.8 PO EX, SH PAC-09BO-056-09 B 2 4 ODO MO2 LO 1.5 1.5 SD EX, RT PAC-09BO-057-01 B 2 4 UNIM UNI F 2 1–2 PO EX, RT PAC-09BO-058-01 B 4 4 UNI UNI F 11 <1 PO EX PAC-09BO-058-02 B 4 4 UNIM UNI F 9 1–2 PO EX PAC-09BO-058-03 B 4 4 UNIM UNI F 3 1–2 PO EX PAC-09BO-058-04 B 4 4 LTM LBF F 1 5.9 1.9 PO EX PAC-09BO-058-05 B 4 4 ARM SHL F 1 0.8 0.6 DA EX PAC-09BO-058-06 B 4 4 TAY PH1 PE 1 U 0.9 0.8 PO EX PAC-09BO-058-07 B 4 4 ODO MAL F L 1 FU 1.6 1.3 PO EX, RT PAC-09BO-058-08 B 4 4 ODO DP4 LO R 1 YEA 1.4 0.9 PO EX PAC-09BO-058-09 B 4 4 CER MO-PM UP 1 1.1 0.6 DA EX, RT PAC-09BO-059-01 B 4 5 UNIM UNI F 1 <1 PO EX PAC-09BO-059-02 B 4 5 UNIM UNI F 3 1–2 PO EX PAC-09BO-059-03 B 4 5 MTM-LTM LBF F 1 5.7 1.3 DA EX, RT, CRK, GN PAC-09BO-059-04 B 4 5 LTM LBF F 7.8 1.7 PO EX, RT PAC-09BO-059-05 B 4 5 ODO MTC PE+PS L 1 FU 6.7 2.4 PO EX, RT PAC-09BO-059-06 B 4 5 ODO AST W R 1 FU 3.6 2.3 DA EX, RT, GN PAC-09BO-059-07 B 4 5 ODO MTC DS L 1 5.6 1.3 PO EX, RT, CRK, STG PAC-09BO-059-08 B 4 5 GAL FIB PE R 1 1.5 0.8 DA EX, RT, STG 1 Fusion Max width Unit R Count Max length Plaza YEA 1 U 230 Max length Max width 1 2.5 1.2 1 1–2 1 1–2 1 4.3 F 1 UNI F UNI UNI UNIM LBF PAF PMX PRO 4 ODO NVB F 10 4 UNIM UNI F 3 1–2 10 4 UNIM LBF F 1 2.7 0.9 A 1 5 GOP FEM PE+PS+DE 2.3 1.3 SD PAC-10BO-007-01 A 1 5 UNIM UNI F PAC-10BO-014-01 B 3 5 UNIM UNI F PAC-10BO-014-03 B 3 5 ODO MAL F L 1 PAC-10BO-014-04 B 3 5 IGU CDV F AX 1 PAC-10BO-014-05 B 3 5 MAZ PH1 DE+S PAC-10BO-014-06 B 3 5 MUS MAN+LM2 F R PAC-10BO-014-07 B 3 5 ODO MO3 UP L PAC-10BO-014-08 B 3 5 UNIM UNI PAC-10BO-020-01 B 5 5 UNI PAC-10BO-020-02 B 5 5 PAC-10BO-020-03 B 5 5 PAC-10BO-020-04 B 5 PAC-10BO-020-05 B PAC-10BO-020-08 B Catalogue number Plaza Unit Level ID Bone End Side Count PAC-09BO-060-01 B 10 4 DOG HUM PS L PAC-09BO-061-01 B 10 4 UNIM UNI F PAC-09BO-062-01 B 10 4 UNIM UNI F PAC-09BO-062-02 B 10 4 ODO TIB DS PAC-09BO-063-01 B 10 4 UNI UNI PAC-09BO-063-02 B 10 4 UNIM PAC-09BO-063-03 B 10 4 PAC-09BO-063-04 B 10 4 PAC-09BO-063-05 B 10 4 PAC-09BO-063-06 B 10 PAC-09BO-064-01 B PAC-09BO-064-02 B PAC-10BO-006-01 Fusion Surface Taphonomy state PO EX PO EX PO EX PO EX, RT <1 PO EX 2 1–2 PO EX F 1 1.3 0.4 PO BUR F 1 1.6 1.1 PO EX, RT L 1 1.8 0.9 SD EX L 1 1.8 1.4 PO EX PO EX PO EX, RT R R 1 FU FU 1 2.0 3–4 6 EX, RT DA EX 1.5 1.1 SD EX 1.1 0.7 SD EX 2.0 0.7 DA SH, CRK 1 1.8 0.8 SD EX 1 1.5 1.2 SD EX, RT F 1 <1 DA EX UNI F 1 <1 PO EX UNIM UNI F 3 1–2 DA EX, STG UNIM UNI F 2 2–3 PO EX 5 UNIM UNI F 1 1.2 0.8 SD RT, BUR 5 5 LTM LBF F 1 5.4 1.2 PO EX, RT 5 5 TAY FEM PE 1.4 0.7 DA EX 1 L 1 1–2 PO FU FU FU 231 Catalogue number Max length Max width 1 1.8 1.4 DA EX 1 1.1 0.9 PO EX, RT 1.0 0.7 SD EX 4.1 2.2 SD EX, RT, STG 1.9 0.9 PO EX, RT, STG PO EX Plaza Unit Level ID Bone End Side Count Fusion PAC-10BO-020-09 B 5 5 ODO RIB F L PAC-10BO-020-10 B 5 5 ODO MO UP PAC-10BO-020-11 B 5 5 ODO MO-PM UP R 1 PAC-10BO-029-01 B 6 5 ODO TIB DS+DE L 1 FU PAC-10BO-029-02 B 6 5 RAB INN ACE L 1 FU PAC-10BO-030-01 B 6 5 UNI UNI F PAC-10BO-030-02 B 6 5 UNIM UNI F PAC-10BO-030-03 B 6 5 MAZ NVB W PAC-10BO-031-01 B 6 5 UNI UNI F 4 PAC-10BO-031-02 B 6 5 UNIM UNI F PAC-10BO-031-03 B 6 5 UNIM UNI PAC-10BO-031-04 B 6 5 MTM-LTM LBF PAC-10BO-031-05 B 6 5 LTM PAC-10BO-031-06 B 6 5 PAC-10BO-031-07 B 6 PAC-10BO-037-01 B 8 PAC-10BO-039-01 B PAC-96BO-065-01 2 <1 1 PO EX, RT DA EX, RT <1 PO EX 4 1–2 PO EX F 2 2–3 PO EX, RT F 1 4.4 0.8 PO EX, RT LBF F 1 3.6 1.6 PO EX ODO MO3 LO R 1 ADU 2.3 0.9 DA EX 5 ODO MO1-2 LO R 1 YEA 5 ODO PH2 PE+PS 9 5 VIP VER F B 2b 3 UNIM UNI PAC-96BO-065-02 B 2b 3 UNIM PAC-96BO-065-03 B 2b 3 ODO PAC-96BO-069-01 B 3c 4 PAC-96BO-069-02 B 3c 4 PAC-96BO-069-03 B 3c 4 PAC-96BO-069-05 B 3c 4 PAC-96BO-069-06 B 3c 4 PAC-96BO-073-01 B 1 PAC-96BO-074-01 B 8 R 1 1–2 Surface Taphonomy state FU 2.0 1.5 2.3 1.0 DA EX 1 2.0 1.5 PO EX 1 1.0 0.9 PO EX F 2 2–3 PO EX, RT UNI F 1 PH1 DE 1 UNI UNI F 1 UNIM UNI F UNIM UNI MTM-LTM LBF LTM 3 3 AX 3.2 0.9 PO EX, RT, BUR 1.7 1.0 PO EX <1 PO EX 1 1–2 PO EX F 2 1–2 PO EX F 1 3.2 1.6 PO EX, RT LBF F 1 5.9 2.1 PO EX, RT UNIM UNI F 1 2–3 PO EX, RT UNI UNI F 3 <1 PO EX FU 232 Catalogue number Side Surface Taphonomy state Level ID Bone End PAC-96BO-074-02 B 8 3 UNIM UNI F 9 1–2 PO EX, RT PAC-96BO-074-03 B 8 3 UNIM UNI F 2 2–3 PO EX, RT PAC-96BO-074-07 B 8 3 MTM-LTM LBF F 1 3.9 1.2 DA EX, RT PAC-96BO-074-10 B 8 3 ODO FEM PS 1 3.5 1.9 PO EX PAC-96BO-077-01 B 3 3 UNIM UNI F 1 3–4 SD EX, BUR PAC-96BO-078-01 B 3b 3 LTM UNI F 1 3.5 PO EX, RT PAC-96BO-079-01 B 11 3 UNI UNI F 1 <1 DA EX PAC-96BO-079-02 B 11 3 STM LBF F 1 1.5 PO EX, RT PAC-96BO-080-01 B 6 3 UNIM UNI F 1 <1 PO EX PAC-96BO-080-02 B 6 3 MAZ MTT DS 1 1.8 0.8 PO EX PAC-96BO-080-03 B 6 3 ODO FEM DE R 1 FU 2.8 1.8 PO EX, CRK PAC-96BO-080-04 B 6 3 ARM PH1 W L 1 FU 0.6 0.5 DA EX PAC-96BO-080-05 B 6 3 COL VER W AX 1 1.0 0.9 PO EX PAC-96BO-080-06 B 6 3 COL VER W AX 1 1.0 0.9 PO EX PAC-96BO-080-07 B 6 3 COL VER W AX 1 1.0 1.0 PO EX PAC-96BO-081-01 B 3 5 UNI UNI F 3 <1 PO EX, RT PAC-96BO-081-02 B 3 5 UNIM UNI F 16 1–2 PO EX, RT PAC-96BO-081-03 B 3 5 UNIM UNI F 5 2–3 PO EX PAC-96BO-081-04 B 3 5 MTM-LTM LBF F 1 2.9 1.2 PO EX, RT PAC-96BO-081-05 B 3 5 MTM-LTM LBF F 1 2.9 1.1 PO EX, RT PAC-96BO-081-07 B 3 5 ODO MTC PE+PS+MS L 1 FU 11.1 2.2 SD EX, RT, GN PAC-96BO-081-08 B 3 5 ODO LMV F AX 1 FU 1.0 0.9 PO EX PAC-96BO-081-09 B 3 5 ODO PH2 PE 1 FU 1.2 1.0 SD PAC-96BO-081-10 B 3 5 LTM LBF F 1 5.4 1.8 DA EX, RT PAC-96BO-082-01 B 3d 2 ARM TIB MS+DS 1 2.5 0.8 PO EX, RT, STG PAC-96BO-083-01 B 6 5 UNI UNI F 3 <1 PO EX PAC-96BO-083-02 B 6 5 UNIM UNI F 4 1–2 PO EX L Fusion Max width Unit L Count Max length Plaza 1.6 0.3 233 Catalogue number Side Count Fusion Max length Max width Plaza Unit Level ID Bone End PAC-96BO-083-03 B 6 5 UNIM UNI F PAC-96BO-083-05 B 6 5 ODO MTT PE L 1 FU 2.0 1.7 PAC-96BO-083-06 B 6 5 ODO DP4 LO L 1 FAW 1.5 PAC-96BO-083-07 B 6 5 ODO MO1 LO L 1 YEA 1.9 PAC-96BO-085-01 B 4 3 UNIM UNI F 1 PAC-96BO-086-01 B 5 3 UNIM UNI F PAC-96BO-087-01 B 6 2 UNIM UNI PAC-96BO-088-01 B 3b 2 UNIM UNI PAC-96BO-089-01 B 9 3 ODO FEM DS PAC-96BO-090-01 B 3b 4 UNI UNI PAC-96BO-090-02 B 3b 4 UNI PAC-96BO-090-03 B 3b 4 UNIM PAC-96BO-090-04 B 3b 4 PAC-96BO-090-06 B 3b PAC-96BO-091-01 B PAC-96BO-091-03 B PAC-96BO-092-01 1 SD EX, RT DA EX 0.7 SD EX 0.8 DA EX 2–3 PO EX, RT 1 2–3 PO EX, RT F 1 3–4 PO EX, RT F 1 1.6 0.9 SD RT, BUR 1 5.3 2.3 DA EX F 1 <1 PO EX UNI F 2 1–2 PO EX UNI F 2 1–2 DA EX UNIM UNI F 1 3–4 PO EX, RT 4 LTM LBF F 1 3.9 PO EX, RT 2d 4 UNIM UNI F 2 2d 4 ARM MTC DE+DS 1 B 6 3 MTM-LTM LBF F PAC-96BO-093-01 B 5 4 KIN SHL PAC-96BO-094-01 B 6 5 UNI PAC-96BO-094-02 B 6 5 UNIM PAC-96BO-094-03 B 6 5 PAC-96BO-094-04 B 6 PAC-96BO-094-06 B PAC-96BO-094-07 B PAC-96BO-095-01 L 3–4 Surface Taphonomy state 1.5 1–2 DA EX 0.7 0.5 DA EX 1 4.2 1.2 PO EX, RT F 1 1.4 1.0 PO EX UNI F 9 <1 DA EX UNI F 3 1–2 DA EX, RT UNIM UNI F 1 2–3 PO EX 5 UNIM UNI F 1 2–3 PO EX, RT 6 5 ARM SHL F 1 0.5 0.5 DA EX 6 5 CER MO-PM F 1 1.0 0.5 SD RT B 13 5 UNIM UNI F 1 1–2 PO EX PAC-96BO-095-02 B 13 5 UNIM UNI F 1 2–3 PO EX PAC-96BO-096-01 B 2d 5 UNI UNI F 1 <1 PO EX FU 234 Catalogue number Side Surface Taphonomy state Level ID Bone End PAC-96BO-096-02 B 2d 5 UNIM UNI F 4 1–2 DA EX PAC-96BO-097-01 B 6 5 UNIM UNI F 1 2–3 SD EX PAC-96BO-098-01 B 7 5+6 UNIM UNI F 1 2–3 DA EX PAC-96BO-098-02 B 7 5+6 ODO MTT DS R 1 3.7 1.7 PO EX, CRK PAC-96BO-098-03 B 7 5+6 ODO RIB POST R 1 2.4 1.3 SD EX PAC-96BO-101-01 B 5 5 UNI UNI F 3 <1 DA EX PAC-96BO-101-02 B 5 5 UNIM UNI F 5 1–2 DA EX PAC-96BO-101-03 B 5 5 UNIM LBF F 1 2–3 SD EX PAC-96BO-101-04 B 5 5 ARM SHL F 1 0.7 0.5 DA EX PAC-96BO-101-05 B 5 5 ODO GC F 1.7 0.9 SD EX PAC-96BO-101-07 B 5 5 LTM LBF F 1 6.5 1.2 PO EX, RT, SH PAC-96BO-102-01 B 11 3 UNI UNI F 1 1–2 PO EX, RT PAC-96BO-104-01 B 10 4 UNIM UNI F 1 2–3 PO EX PAC-96BO-104-02 B 10 4 UNIM UNI F 1 3–4 PO EX PAC-96BO-104-03 B 10 4 MTM-LTM LBF F 2.3 1.0 PO EX PAC-96BO-104-04 B 10 4 ODO TRQ W R 1 FU 2.1 1.4 PO EX PAC-96BO-104-05 B 10 4 ODO MAL W L 1 FU 1.6 1.5 SD EX PAC-96BO-106-01 B 2c 5 UNIM UNI F 1 1–2 PO EX PAC-96BO-106-02 B 2c 5 UNIM UNI F 2 1–2 PO EX PAC-96BO-106-03 B 2c 5 ARM SHL F 1 0.7 0.5 SD EX PAC-96BO-106-04 B 2c 5 ODO MTT PE 2.0 0.8 DA EX PAC-96BO-122-01 B 1 5 UNI UNI F 1 <1 PO EX PAC-96BO-122-02 B 1 5 UNIM UNI F 2 1–2 PO EX PAC-96BO-123-01 B 3d 5 UNIM UNI F 1 2–3 PO EX, CRK PAC-96BO-123-02 B 3d 5 LTM LBF F 1 2.9 1.5 DA EX, RT, PN PAC-96BO-123-03 B 3d 5 LTM LBF F 1 3.6 1.6 PO EX PAC-96BO-123-04 B 3d 5 MTM-LTM LBF F 1 2.9 0.7 DA SH, CRK, STG 1 Fusion Max width Unit R Count Max length Plaza FU U 1 R 1 FU 235 Max length Max width 1 0.6 0.5 F 3 <1 UNI F 3 1–2 LBF F 1 2.9 UNI F 1 UNI F UNIM UNI LTM LBF 5 UNIM 4 5 B 8 B 8 PAC-96BO-129-03 B PAC-96BO-129-04 Catalogue number Plaza Unit Level ID Bone End PAC-96BO-124-01 B 3 5 ARM SHL F PAC-96BO-125-01 B 3 5 UNI UNI PAC-96BO-125-02 B 3 5 UNIM PAC-96BO-125-03 B 3 5 UNIM PAC-96BO-126-01 B 2b 5 UNIM PAC-96BO-127-01 B 7 5+6 UNIM PAC-96BO-127-02 B 7 5+6 PAC-96BO-127-03 B 7 5+6 PAC-96BO-128-01 B 4 PAC-96BO-128-02 B PAC-96BO-129-01 PAC-96BO-129-02 Side Count Fusion Surface Taphonomy state IT BUR DA EX PO EX PO EX 1–2 PO EX 3 1–2 PO EX F 1 4–5 DA EX F 1 6.8 SD EX, RT LBF F 1 2–3 PO EX ODO FEM DE PO EX 5 UNI UNI F 2 <1 DA EX 5 UNIM UNI F 6 1–2 PO EX 8 5 UNIM UNI F 1 3–4 PO EX, CRK B 8 5 OPOV MAN F L 1 1.3 0.9 PO EX PAC-96BO-129-05 B 8 5 ARM RAD PE+PS+MS R 1 2.0 0.4 PO EX, RT PAC-96BO-129-06 B 8 5 ODO MO UP R 1 1.5 1.0 PO EX PAC-96BO-129-07 B 8 5 STM LBF F 1 1.2 0.5 DA SH PAC-96BO-130-01 B 12 5 UNIM UNI F 1 2–3 DA EX PAC-96BO-130-02 B 12 5 LTM LBF F 1 3.6 1.7 PO EX, SH PAC-96BO-130-03 B 12 5 LTM UNI F 1 3.0 1.7 PO EX PAC-96BO-131-01 B 10 5 STM LBF F 1 2.2 0.5 DA EX, GN PAC-96BO-131-02 B 10 5 CAT PH1 DE+DS 1 0.6 0.6 SD PAC-96BO-133-01 B 7 5 UNIM UNI F PAC-96BO-134/141-01 B 1 5 ODO HUM DS PAC-96BO-137-01 B 11 3 UNIM UNI PAC-96BO-138-01 B 1 3 UNIM PAC-96BO-138-02 B 1 3 UNIM L 1 FU FU 2.2 1 3–4 1 5.2 F 1 UNI F UNI F R 1.0 1.7 2.0 PO EX, RT PO EX, RT, SH 1–2 PO EX 2 <1 PO EX 1 1–2 PO EX, CRK 1.7 236 Catalogue number Side Count Fusion Max length Max width Surface Taphonomy state Plaza Unit Level ID Bone End PAC-96BO-139-01 B 1 4 UNI UNI F 1 <1 PO EX PAC-96BO-140-01 B 1 5 UNIM UNI F 3 1–2 DA EX PAC-96BO-140-02 B 1 5 UNIM UNI F 1 1–2 PO EX PAC-96BO-140-03 B 1 5 LTM LBF F 1 4.8 PO EX, SH, CRK PAC-96BO-141-01 B 1 5 UNI UNI F 2 <1 SD EX PAC-96BO-141-02 B 1 5 UNI UNI F 1 <1 PO EX PAC-96BO-141-03 B 1 5 UNIM UNI F 1 <1 PO EX PAC-96BO-141-04 B 1 5 UNIM UNI F 1 1–2 DA EX, RT PAC-96BO-141-05 B 1 5 UNIM UNI F 1 1–2 PO EX PAC-96BO-144-01 B 2b 4 UNIM UNI F 1 <1 PO EX PAC-96BO-145-01 B 3b 4 UNIM UNI F 1 1–2 PO EX PAC-96BO-146-01 B 3 5 UNI UNI F 1 <1 PO EX PAC-96BO-150-01 B 5 5 UNIM UNI F 1 1–2 PO EX, RT PAC-96BO-150-02 B 5 5 STM-MTM LBF F 1 2.3 SD RT PAC-96BO-152-01 B 6 5 UNIM UNI F 1 1–2 PO EX PAC-96BO-152-02 B 6 5 ODO MTP S 1 1.3 0.7 SD RT, STG PAC-96BO-152-03 B 6 5 TES SHL F 1 0.8 0.6 DA EX PAC-96BO-153-01 B 7 3+5 UNIM UNI F 2 1–2 PO EX PAC-96BO-154-01 B 7 3 UNIM UNI F 1 2–3 PO EX PAC-96BO-155-01 B 8 3 UNI UNI F 1 <1 PO EX PAC-96BO-155-02 B 8 3 UNIM UNI F 8 1–2 PO EX PAC-96BO-155-04 B 8 3 UNIM UNI F 1 2–3 PO EX PAC-96BO-155-05 B 8 3 TAY PH2 W PAC-96BO-155-06 B 8 3 MAZ HUM DE PAC-96BO-155-07 B 8 3 MTM-LTM LBF F PAC-96BO-156-01 B 8 5/6B UNI UNI PAC-96BO-156-02 B 8 5/6B UNI UNI 1.2 0.7 1 FU 1.6 1.0 PO EX, RT, GN 1 FU 1.5 1.3 PO EX 1 4.9 0.6 PO EX, RT F 4 <1 DA EX F 3 1–2 DA EX L 237 Catalogue number Side Count Fusion Max length Max width Surface Taphonomy state Plaza Unit Level ID Bone End PAC-96BO-156-03 B 8 5/6B UNI UNI F PAC-96BO-156-04 B 8 5/6B TAY NAV W PAC-96BO-159-01 B 9 5 UNI UNI F 6 PAC-96BO-159-02 B 9 5 UNIM UNI F 2 PAC-96BO-159-03 B 9 5 ODO PH2 W 1 FU 3.0 PAC-96BO-159-05 B 9 5 TAY PH2 W 1 FU 1.7 PAC-97BO-002-01 B 97-U5 3 UNI UNI F 10 <1 PO PAC-97BO-002-02 B 97-U5 3 UNIM UNI F 9 <1 PO PAC-97BO-002-03 B 97-U5 3 UNI UNI F 1 1–2 PO PAC-97BO-002-04 B 97-U5 3 UNIM UNI F 1 2–3 PO PAC-97BO-002-05 B 97-U5 3 UNIM UNI F 1 1–2 PO EX PAC-97BO-002-06 B 97-U5 3 UNIM UNI F 1 2–3 PO EX PAC-97BO-002-07 B 97-U5 3 UNIM UNI F 1 2–3 SD EX PAC-97BO-002-08 B 97-U5 3 ODO FEM DE L 1 FU PAC-97BO-002-09 B 97-U5 3 ODO FEM PE L 1 FU PAC-97BO-002-10 B 97-U5 3 ODO FEM PS+MS+DS L 1 PAC-97BO-002-11 B 97-U5 3 ODO CAL DE+DS+MS R 1 PAC-97BO-002-12 B 97-U5 3 ODO HUM DS L 1 PAC-97BO-002-13 B 97-U5 3 ODO AST F R 1 PAC-97BO-003-01 B 97-U2 3 UNIM UNI F 1 <1 PAC-97BO-003-02 B 97-U2 3 UNI UNI F 1 PAC-97BO-003-03 B 97-U2 3 UNIM UNI F PAC-97BO-004-01 B 97-SU1 3 UNIM UNI PAC-97BO-004-02 B 97-SU1 3 UNIM UNI PAC-97BO-004-04 B 97-SU1 3 UNIM PAC-97BO-005-01 B 97-U4 3 PAC-97BO-005-02 B 97-U4 3 1 R 1 2–3 FU DA EX, RT PO EX, RT <1 PO EX 1–2 PO EX 1.3 PO EX, GN 1.0 PO EX 1.7 1.1 EX 5.5 5.3 DA EX, RT, CT, GN 4.5 3.1 DA EX, RT, GN 21.2 4.8 DA EX, RT, CRK 6.3 2.3 DA EX 5.5 1.8 SD EX 1.6 1.5 SD EX PO EX <1 PO EX 1 1–2 PO EX F 2 1–2 PO EX F 1 1–2 DA EX UNI F 1 2–3 PO EX, RT UNI UNI F 1 <1 PO EX UNI UNI F 2 1–2 PO EX FU FU 238 Catalogue number Side Surface Taphonomy state Level ID Bone End PAC-97BO-006-01 C 97C5 4 UNIM UNI F 4 <1 PO EX PAC-97BO-006-02 C 97C5 4 UNIM UNI F 4 <1 PO EX PAC-97BO-006-03 C 97C5 4 UNIM UNI F 1 1–2 SD EX PAC-97BO-006-04 C 97C5 4 UNIM UNI F 2 1–2 DA EX, CRK PAC-97BO-006-05 C 97C5 4 UNIM UNI F 1 1–2 PO EX PAC-97BO-006-06 C 97C5 4 LTM UNI F 1 3.3 PO EX, CRK PAC-97BO-009-01 C 97C2 4 UNIM UNI F 1 3–4 DA EX PAC-97BO-010-01 B 97-RU1 5 UNIM UNI F 1 1–2 DA EX PAC-97BO-010-02 B 97-RU1 5 UNIM UNI F 1 1–2 SD EX PAC-97BO-010-03 B 97-RU1 5 UNIM UNI F 1 2–3 PO EX PAC-97BO-012-01 B 97-RU1 3 UNIM UNI F 1 1–2 PO EX PAC-97BO-012-02 B 97-RU1 3 UNIM UNI F 1 2–3 PO EX PAC-97BO-013-01 B 97-SU4 3 UNIM UNI F 1 1–2 PO EX PAC-97BO-019-01 B 97-U3 3 UNIM UNI F 1 <1 PO EX PAC-97BO-019-02 B 97-U3 3 UNIM UNI F 3 1–2 PO EX PAC-97BO-019-03 B 97-U3 3 UNIM UNI F 1 1–2 PO EX PAC-97BO-019-04 B 97-U3 3 UNIM UNI F 2 1–2 SD EX PAC-97BO-019-05 B 97-U3 3 UNIM UNI F 1 2–3 DA EX PAC-97BO-019-06 B 97-U3 3 ARM SHL F 1 0.7 0.6 PO EX PAC-97BO-020-02 C 97C5 5 UNIM UNI F 1 1.9 1.4 DA EX, RT PAC-97BO-020-03 C 97C5 5 UNIM UNI F 1 1–2 PO EX PAC-97BO-020-04 C 97C5 5 UNIM UNI F 1 2–3 PO EX PAC-97BO-023-01 B 97-U4 5 UNI UNI F 5 <1 PO EX PAC-97BO-023-02 B 97-U4 5 UNIM UNI F 9 1–2 PO EX PAC-97BO-023-03 B 97-U4 5 UNIM UNI F 1 1–2 SD EX, RT, STG PAC-97BO-023-04 B 97-U4 5 UNIM UNI F 1 2–3 PO EX, RT PAC-97BO-023-06 B 97-U4 5 ODO RIB F DA EX 1 Fusion Max width Unit R Count Max length Plaza FU 2.0 1.1 0.9 239 Max length Max width 1 1.0 0.8 F 1 1–2 UNI F 1 1–2 PO EX UNI F 1 <1 DA EX UNIM UNI F 1 1–2 DA EX 3 UNIM UNI F 1 3–4 SD EX 97-SU5 4 UNIM UNI F 2 1–2 PO EX 97-SU5 4 UNIM UNI F 1 2–3 PO EX B 97-SU5 4 UNIM UNI F 1 3–4 PO EX PAC-97BO-033-01 B 97-SU5 3 UNIM UNI F 3 <1 PO EX PAC-97BO-033-02 B 97-SU5 3 UNIM UNI F 3 1–2 PO EX PAC-97BO-036-01 B 97-TU1 3 UNIM UNI F 1 <1 PO EX PAC-97BO-036-02 B 97-TU1 3 UNIM UNI F 1 1–2 PO EX PAC-97BO-036-03 B 97-TU1 3 UNIM UNI F 1 1–2 SD EX PAC-97BO-036-04 B 97-TU1 3 UNIM UNI F 1 2–3 DA EX PAC-97BO-039-01 B 97-U4 5 UNI UNI F 5 <1 PO EX PAC-97BO-039-02 B 97-U4 5 UNIM UNI F 3 1–2 SD EX PAC-97BO-039-03 B 97-U4 5 UNIM UNI F 2 1–2 DA EX, RT, CRK PAC-97BO-039-04 B 97-U4 5 UNIM UNI F 5 2–3 PO EX, RT PAC-97BO-039-05 B 97-U4 5 UNIM UNI F 1 3–4 PO EX PAC-97BO-039-06 B 97-U4 5 UNIM UNI F 1 2.0 1.4 PO RT, BUR PAC-97BO-039-12 B 97-U4 5 MTM MAX F R 1 2.2 1.7 DA EX PAC-97BO-039-13 B 97-U4 5 ARM TIB DS+MS L 1 3.3 0.9 PO EX, STG PAC-97BO-040-01 B 97-U4 4 UNIM UNI F 1 2–3 PO EX PAC-97BO-040-02 B 97-U4 4 OPOM FEM PS+MS+DS 1 4.2 PO EX, RT, STG PAC-97BO-041-01 B 97-U4 4 UNIM UNI F 1 1–2 PO EX, CRK PAC-97BO-041-02 B 97-U4 4 UNIM UNI F 1 3–4 PO EX, RT Catalogue number Plaza Unit Level ID Bone End PAC-97BO-023-07 B 97-U4 5 TES SHL F PAC-97BO-024-01 B 97-TU4 5 UNIM UNI PAC-97BO-024-02 B 97-TU4 5 UNIM PAC-97BO-028-01 B 97-TU2 3 UNIM PAC-97BO-028-02 B 97-TU2 3 PAC-97BO-028-03 B 97-TU2 PAC-97BO-032-01 B PAC-97BO-032-02 B PAC-97BO-032-03 Side R Count Fusion Surface Taphonomy state PO EX, RT IT 0.6 240 Catalogue number Max length Max width 1 4.0 1.3 SD RT 1 2.8 1.0 PO EX 3.1 2.1 PO EX, CRK 4.9 2.4 PO EX, RT, GN 1 2.5 0.7 PO EX, RT, CRK, STG 1 2.2 0.4 PO RT, CRK, STG 0.8 0.6 PO EX 3.6 1.5 PO EX, RT PO EX IT BUR <1 DA EX 1–2 PO EX 1–2 PO EX, RT 1–2 DA EX 7 <1 SD EX 5 1–2 PO EX F 1 1–2 SD EX, RT UNI F 1 2–3 DA EX, CRK UNI F 1 <1 DA EX Plaza Unit Level ID Bone End Side PAC-97BO-041-03 B 97-U4 4 LTM LBF F PAC-97BO-041-04 B 97-U4 4 LTM UNI F PAC-97BO-043-01 B 97-U5 3 ODO HUM DS R 1 PAC-97BO-043-02 B 97-U5 3 ODO HUM DE+DS R 1 PAC-97BO-043-03 B 97-U5 3 MTM-LTM UNI F PAC-97BO-043-04 B 97-U5 3 MTM-LTM UNI F PAC-97BO-045-01 B 97-SU9 4 RAB NAV W PAC-97BO-050-01 B 97-U1 5 LTM LBF F 1 PAC-97BO-054-01 B 97-TU2 5 UNIM UNI F <1 PAC-97BO-055-01 B 97-SU4 4 UNIM LBF F 1 1 PAC-97BO-057-01 B 97-SU2 3 UNIM UNI F 1 PAC-97BO-058-01 B 97-SU2 4 UNIM UNI F 1 PAC-97BO-060-01 C 97C1 3 UNIM UNI F 1 PAC-97BO-062-01 B 97-SU3 4 UNIM UNI F 1 PAC-97BO-063-01 B 97-SU2 3 UNIM UNI F PAC-97BO-063-02 B 97-SU2 3 UNIM UNI F PAC-97BO-063-03 B 97-SU2 3 UNIM UNI PAC-97BO-063-04 B 97-SU2 3 UNIM PAC-97BO-133-01 B 97-SU2 3 UNI L Count 1 Fusion FU FU 1.0 0.5 Surface Taphonomy state 241 Table A.3 Pacbitun dataset for the transitional period late Middle Preclassic-early Late Preclassic Catalogue number Plaza Unit Level ID Bone End PAC-10BO-012-01 A 2 4 UNI UNI F PAC-10BO-012-02 A 2 4 MAZ MTT PE+PS+MS PAC-10BO-012-03 A 2 4 ODO PH2 PAC-10BO-013-01 A 2 4 UNI UNI PAC-10BO-013-02 A 2 4 ODO PH2 Side Count Fusion 1 L Max length Max width 1–2 Surface state Taphonomy PO EX 1 FU 6.6 1.2 PO EX, RT, CRK W 1 FU 3.3 1.9 DA EX, RT, GN F 1 PO EX W 1 PO EX <1 FU 2.6 1.4 242