Survey
* Your assessment is very important for improving the workof artificial intelligence, which forms the content of this project
* Your assessment is very important for improving the workof artificial intelligence, which forms the content of this project
Journal of Mammalogy, 84(2):418–430, 2003 USING MORTALITY PROFILES TO INFER BEHAVIOR IN THE FOSSIL RECORD TERESA E. STEELE* Department of Anthropological Sciences, 450 Serra Mall, Building 360, Stanford University, Stanford, CA 94305-2117, USA Mortality profiles can be used to investigate modes of accumulation of fossil assemblages, including predation by ancient nonhuman and human (Homo) hunters. Prey age at death reflects hunting decisions and opportunities in terms of calories returned for energy spent and risks taken. Nonhuman carnivores commonly harvest vulnerable individuals (young and old), whereas humans consistently can take prime adults. As an example of how mortality profiles can be used to illuminate predator behavior, this article examines when the ability to select prime-age animals emerged during human behavioral evolution. Although it would be expected that the appearance of this behavior coincided with the appearance of morphologically and archaeologically modern humans, analyses of archaeological assemblages from western Europe and South Africa suggest that this trait was already present in archaic people who preceded modern humans. Studying age distributions in fossil assemblages is not without its limitations, including the difficulty of estimating age at death in fossil specimens, pre- and postdepositional biases, and reconstructing the age structure and behavior of prey herds. Nevertheless, valuable behavioral information can be gained by using controlled comparisons of many assemblages. Key words: age–structure analysis, Canis lupus, Cervus elaphus, elk, human evolution, hunting strategies, mortality profiles, predation, wolves Hunters, both human (Homo) and nonhuman, make decisions about which prey to pursue by considering which individuals will provide the highest return rate, usually calories, per unit of time or energy spent foraging (Stephens and Krebs 1986). In addition to calories, predators may also consider risks involved in hunting, such as the possibility of spending too much time for energy return in searching for prey, the likelihood that prey will injure hunters, and for humans, the number of hunting implements that might be lost (Frison 1991). Consequently, prey that hunters capture provides information on hunting strategy and prey choice. In species where males are larger than females, prime males will provide the most calories of any age or sex group; however, risks to the hunter may make males unobtainable or less attractive. These risks may dictate the targeting of more vulnerable individuals, such as the diseased, injured, senile, or young. Consequently, data on age at death provide information about how readily a hunter can take the strongest, or prime, animals versus the weakest or most vulnerable individuals, usually the young and old. A hunter of prime animals must be either stronger or faster than the prey or skilled enough (meaning technologically sophisticated for humans) to reduce risks of injury and increase the probability that the animal will be taken. Because of these trade-offs, analyses of ages-at-death distributions, or mortality profiles, and prey in fossil assemblages can provide information on predator behavior. * Correspondent: [email protected] 418 May 2003 SPECIAL FEATURE—MAMMALIAN PALEONTOLOGY Analyses of mortality profiles found in archaeological assemblages potentially can provide information on human behavioral evolution, because of differences in the way that humans and other nonhuman predators select prey. Humans are unique in consistently selecting prime-age prey, and therefore, identifying when humans first developed this ability could signal significant changes in human language ability, cognitive function, or cultural capacity. Modern humans (Homo sapiens) dispersed from Africa approximately 40,000–50,000 years ago and are associated with the Upper Paleolithic, which is characterized in the archaeological record by having more numerous sites, more intensely occupied sites, standardized but diverse tools, tools made out of bone and ivory, art objects, and items of personal adornment (Klein 1999). It is reasonable to expect that the ability to consistently hunt prime animals also emerged 40,000–50,000 years ago. MATERIALS AND METHODS Numerous methods exist for assessing age at death of skeletal specimens (for reviews see Amorosi 1989; Morris 1972; Pike-Tay 2000; Wilson et al. 1982); analyses of epiphyseal fusion and tooth eruption are most commonly used (Klein and Cruz-Uribe 1984; O’Connor 2000; Reitz and Wing 1999). Age at death can be estimated from teeth using wear stages (e.g., Brown and Chapman 1991b; Lowe 1967; Quimby and Gaab 1957), eruption stages (e.g., Brown and Chapman 1991a), the quadratic–crownheight method (e.g., Klein et al. 1983; Pike-Tay et al. 2000; Spinage 1972), regression equations based on known-age samples (e.g., Klein et al. 1983; Morrison and Whitridge 1997), or cementum annuli data (e.g., Hamlin et al. 2000; Keiss 1969; Mitchell 1967; Pike-Tay 1991; Spinage 1973). Tooth-wear rates may vary between individuals and populations, possibly because of differences in diet (Flook 1970; Hewison et al. 1999; Skogland 1988) or degree of enamel mineralization (Kierdorf and Becher 1997). Visual assessments of wear can be subject to interobserver variation (Hamlin et al. 2000; Keiss 1969; Van Deelen et al. 2000), but the quadratic– 419 crown-height method minimizes this by metrically assessing wear (Steele 2002). Paleobiologists are most interested in the overall shape of a profile, so if there is no systematic bias in age estimations and if age classes are broad, eruption and wear methods should be sufficient. The cementum annuli method is of limited use to archaeologists because of the time, expertise, and equipment involved; because it is frequently applied to incisors in recent specimens, which are often unidentifiable to species and damaged in fossil assemblages; because large samples are necessary to reconstruct a mortality profile accurately; and because most archaeologists are reluctant to destroy irreplaceable fossils (Hamlin et al. 2000; Klein and Cruz-Uribe 1984; PikeTay 1991). To create mortality profiles, age estimates are compiled into histograms or line graphs that show the proportion (either frequency or percentage) of individuals that died in each age class. Age classes are defined depending on precision of age estimation, life histories of species under study, and questions under investigation. For large mammals, age classes commonly are 1 year or groups of years, such as 10% of life span, but any consistent, easily definable, and replicable age classes are suitable. The Kolmogorov–Smirnov test is used to compare the cumulative frequency distributions of 2 histograms (Klein and Cruz-Uribe 1984; Sokal and Rohlf 1995). In species where it is difficult to estimate age at death, raw measurements of tooth crown heights can be compared directly by creating box plots that include 95% confidence interval around sample medians (Klein and Cruz-Uribe 1996; Klein et al. 1999). In some species where body size, and therefore tooth size, differs through time and across space, crown heights can be standardized. Following Kurtén (1953), Van Valen (1964), and Voorhies (1969), paleobiologists use 2 models of idealized mortality profiles, called catastrophic and attritional, to help interpret age distributions found in assemblages. The idealized mortality profiles that I use are from Klein (1982) and are based on a hypothetical population of large mammals that is stationary (size, survival, and fecundity are not changing) and in which females have synchronized birth of 1 offspring/year (Fig. 1). Although variations may occur depending on local conditions or life-history differences such as twinning, the shape of 420 JOURNAL OF MAMMALOGY Vol. 84, No. 2 FIG. 1.—Idealized catastrophic (left) and attritional (right) mortality profiles for a population of large mammals that gives birth to 1 offspring/year and is not changing in size. Dark bars refer to the number of individuals in each age class in a living herd. Hatched bars represent the number of individuals that died between each age class, the attrition on the herd. Hatched bars correspond directly between the 2 histograms. These idealized profiles provide guidelines for comparisons of mortality profiles identified in faunal assemblages. Data from Klein (1982) and Voorhies (1969). these models (i.e., patterns of age-specific mortality) is generally consistent across taxa with similar life histories (Caughley 1966, 1977). The idealized catastrophic profile shows that in a living population, young animals are most abundant and the next age group contains fewer individuals because of high calf mortality. Each subsequent age class has fewer individuals until none remain. This model is called ‘‘catastrophic’’ because it represents the mortality profile that would be found if a stationary herd died at once, shortly after the season’s births (Caughley 1966, 1977; Deevey 1947; Klein 1982). The idealized attritional profile shows the number of individuals that died between each age class to produce the idealized catastrophic profile, and therefore, it is a mathematical derivative of the catastrophic profile. These deaths, caused by disease, malnutrition, and nonhuman predators, are the natural attrition on a herd. This model also has a high number of juvenile individuals, but much fewer adults, although they are still present. Higher mortality in old individuals sometimes produces a rise in the number of individuals in older age classes; thus, the attritional profile sometimes is described as ‘‘Ushaped’’ or ‘‘J-shaped’’ (Caughley 1966; Klein 1982; Levine 1983; Stiner 1990). In a fossil assemblage, an age profile that resembles a living herd might indicate 1 of 4 sit- uations. In a synchronic sample, where all bones are deposited at once, the assemblage might be the result of 1) a natural catastrophe, such as a flood, volcano, or blizzard (Lubinski 2001; Voorhies 1969); or 2) hunters driving an entire herd either into a trap or surround or over a cliff (Frison 1978; Nimmo 1971). In a diachronic assemblage, where bones are accumulated a few at a time, a similar mortality profile might be created by people 3) hunting individual animals, where prey are obtained in proportion to their presence in the herd; or 4) or setting individual traps that are equally successful in trapping animals of all ages. When an age profile that resembles the attritional model is reconstructed in a fossil assemblage, it could represent hunting of the most vulnerable individuals of the herd or scavenging, because scavengers would be eating carcasses produced by attritional factors (Klein 1982, 1994). The idealized catastrophic and attritional profiles are not the only possible age distributions that might be found, and much variation exists in archaeological and paleontological sites. However, these models still provide useful guidelines for interpreting faunal assemblages. Prey availability influences predator choice, and ungulate herds often change locations and sexually segregate, depending on season (Bleich et al. 1997; Bowyer 1984; Geist 1982; Kie and May 2003 SPECIAL FEATURE—MAMMALIAN PALEONTOLOGY Bowyer 1999). High harvest pressure will skew a herd’s age distribution toward younger individuals (Koike and Ohtaishi 1985; McCullough 1979). These changes potentially could influence age profiles of harvested prey. Unfortunately, it is quite difficult to reconstruct prey abundance at specific sites when looking tens of thousands of years into the past, because this would require fundamental assumptions about geomorphology, habitat, and climate, all of which are difficult to reconstruct on such a fine scale. These assumptions are as equally presumptuous as the assumption that the prey population is stationary, although some progress has been made in reconstructing available sex ratios (Berger et al. 2001). Fortunately, in both the archaeological and the paleontological record, time averaging is often the rule (Hadly 1999). Seasonal fluctuations in age structure of the prey species will be averaged out during the course of the year, or if the site was occupied in only 1 season, will be averaged over many years. Fluctuations in age structure over decades or centuries also will be averaged in the prehistorical record, allowing researchers to identify ‘‘typical’’ hunting strategies rather than individual hunting strategies. Fortunately, this is the level of analysis that helps answer paleoecological questions. Prey choice also is influenced by factors other than caloric returns, including chance. Hunters may choose a species because it is more amenable to being herded or driven. Human hunters may choose their prey based on hide quality, which also changes with age or season (e.g., McCabe 1982). Humans may choose to target 1 sex, such as male cervids, because they desire antlers for tools or trophies or canines for ornaments (e.g., d’Errico and Vanhaeren 2002; K. Hamlin, pers. comm.; Pitts 1979). These factors will influence age distributions found in fossil assemblages and can be investigated further as explanations for deviations from the idealized profiles. Once an animal has been harvested, different aged prey may be handled differently, which will affect resulting mortality profiles (Bartram 1993; Bunn 1993; Marean 1997). For example, skulls of adults may be left at the kill site and not returned to camp because they are too heavy, or only skulls of adult male deer may be transported to the campsite or worksite for antler processing. Large mandibles may be broken up for marrow processing, whereas smaller ones re- 421 main whole. Juveniles are more likely to be fully consumed by predators or subsequent scavengers because of their small size and more cartilaginous bones. Thus, juveniles are often underrepresented in faunal assemblages (Binford and Bertram 1977; Blumenschine 1987; Munson 2000). Once material has been deposited in a site, postdepositional destruction will affect large and small (including juveniles of large species) specimens differently (Klein and Cruz-Uribe 1984; Levine 1983; Lyman 1994). This destruction of juvenile remains limits our ability to distinguish hunting focusing on prime adults from that resembling the idealized catastrophic profile. To help control for these limitations, as many age determination methods as feasible should be applied to a fossil assemblage, and mortality profiles should be constructed in multiple ways, such as histograms of estimated ages and box plots comparing raw crown heights. If the results are concordant, then the faunal analyst can be more confident about the mortality profile. Many samples should be compared to see if a robust pattern appears. Additionally, comparing samples with similar postdepositional histories will help control for some biases. Surface qualities of bone and relative abundance of more and less dense postcranial parts can be recorded to elucidate potential differences due to postdeposition destruction. The ratio of isolated teeth to complete mandibles also may provide an indicator of postdepositional destruction. At the least, mortality profiles should be compared with juveniles included and excluded, although some researchers have proposed correction factors to account for biases against juvenile remains (Ducos 2000; Levine 1983; Marean 1997; Munson 1991). HUMAN AND CARNIVORE HUNTING Because the mode of accumulation is known, an example using modern data demonstrates how mortality profiles can be used to infer predator behavior and generate hypotheses for further testing. I reconstructed mortality profiles for 2 samples of Rocky Mountain elk (Cervus elaphus nelsoni) from Wyoming and Montana (Fig. 2). One sample is composed of 98 mandibles of elk killed by wolves (Canis lupus) that were collected by Yellowstone National Park bi- 422 JOURNAL OF MAMMALOGY Vol. 84, No. 2 FIG. 2.—Mortality profiles of Rocky Mountain elk (Cervus elaphus nelsoni) hunted by wolves (Canis lupus; top) and recent humans (Homo sapiens; bottom). Ages for the samples are based on quadratic–crown-height method of estimating age at death from tooth crown heights using dp4 and m1 (see Klein et al. 1983 for more details and formulas). Box plots compare median m1 crown heights for the 2 samples (see Klein and Cruz-Uribe 1996 for discussion of box plots). In both analyses, the 2 samples are significantly different (drawings courtesy of R. Klein). ologists in 1999, primarily from January to May and from October to November. Many remains of calves were badly damaged or fully consumed before park biologists could collect mandibles, so the wolf-kill sample is biased against juveniles (D. Smith, pers. comm.). The other sample consists of 226 mandibles collected from hunter checkpoints in Montana, north of Yellowstone National Park (Hamlin et al. 2000; Quimby and Gaab 1957; C. Wolf collected some data with this sample). I estimated age at death using a method suitable to fossil assemblages—applying the quadratic–crownheight method to dp4 and m1 (Klein and Cruz-Uribe 1984; Klein et al. 1983). I generated histograms with 10% of life-span age classes and considered 21 years to be the potential maximum longevity of individuals from this population (Houston 1982). The wolf-harvested profile is distinct from the idealized catastrophic profile and closely resembles the idealized attritional profile except for the high number of individuals in the oldest age class (19–21 years) in the wolf-kill profile. To further investigate this discrepancy, I offer 3 hypotheses. First, the over-abundance of old individuals is an artifact of the method used to assign age at death because all individuals with May 2003 SPECIAL FEATURE—MAMMALIAN PALEONTOLOGY teeth completely worn away were assigned to the oldest age class. Second, because of the ease of tracking wolves in snow, the wolf-kill sample was collected primarily in winter before young are born in June. The large number of old individuals could represent the easiest winter prey, and other age groups could be targeted at other times of the year. Third, wolves were reintroduced into Yellowstone after an absence of 60 years (Smith et al. 1999). During that time, grizzly bears (Ursus arctos) were the primary predator of elk, but bears killed mainly newborns (Knight et al. 1999; Singer and Mack 1999). If elk population size was increasing during this time, low predation on adults could have allowed an increase in abundance of old elk to beyond what is expected in the model. The human-harvested profile is similar to the idealized catastrophic profile and different from the idealized attritional profile. Human hunters took more individuals in age classes 2 and 3 (2–6 years) than in the catastrophic profile. I hypothesize that 1) hunters preferred the younger adults because of their larger size relative to juveniles, but the inexperience of young adults compared with prime adults made them easier to take; 2) due to heavy hunting for antlers, there could be a limited number of older males available in the prime age classes (K. Hamlin, pers. comm.), and therefore, humans were hunting the next best antler carriers: younger adult males, along with females of any age class; or 3) seasonal hunting regulations imposed by Montana Fish, Wildlife, and Parks dictated the ages of the hunted animals and not hunters’ preference. Mortality profiles for wolf- and humanharvested elk are significantly different when complete profiles are compared (Kolmogorov–Smirnov [K-S], z 5 2.375, P , 0.001). Because the wolf-harvested sample is biased against juveniles, I also compared only adults in the samples. The significant difference remains (K-S, z 5 3.581, P , 0.001). Box plots of the wolf- and human- 423 harvested samples also indicate that wolves were hunting older elk than were humans (Fig. 2). The wolf versus human example shows that humans are more likely to kill adult elk, whereas wolves are more likely to take vulnerable (youngest and oldest) members of the herd. This is not to say that nonhuman predators never hunt prime ungulates; it is well documented that they can take adult animals (Gasaway et al. 1983, 1992; Mech et al. 2001; this study), but they do not harvest them as frequently as do humans (Boyd et al. 1994; Carbyn 1983; Kunkel et al. 1999). Variation is found in this pattern because many local factors influence what ages are harvested at a particular time, such as the age structure of the available herd, predator and prey density, or climatic conditions (Boyd et al. 1994; McCullough 1979; Mech et al. 2001; Van Ballenberghe and Ballard 1997). Klein (1982) also reported a distinction between human and nonhuman hunting when comparing Burchell’s zebra (Equus burchelli) and Cape buffalo (Syncerus caffer) killed by African lions (Panthera leo) in the Serengeti Plains with chamois (Rupicapra rupicapra) killed by modern hunters in the Alps and pronghorn (Antilocapra americana) killed by prehistoric Native Americans in Wyoming. Additionally, comparative data on modern predators assembled by Stiner (1990) indicate that only humans can consistently and exclusively hunt prime animals. McCullough (1979) compared published ages of white-tailed deer (Odocoileus virginianus) harvested by prehistoric hunters in eastern North America with ages of deer killed by wolves in his study area in southern Michigan. The humans harvested more prime adults, whereas the wolves took more juveniles and old individuals. PREHISTORIC HUMAN HUNTING The idealized catastrophic profile assumes that predators are capable of selecting randomly from prey herds, i.e., they are able to harvest all age classes equally. In 424 JOURNAL OF MAMMALOGY reality, skill determines in part which prey actually will be harvested. Modern humans lie at an extreme, because they can focus their hunting on prime-age animals. Below, I use mortality profiles from fossil assemblages to investigate the emergence of this behavior. Acheulean.—The Acheulean stone tool industry began in Africa 1.7–1.5 3 106 years ago, was present in Europe 500,000 years ago, lasted in both places until about 200,000–250,000 years ago, and is associated with H. ergaster or H. erectus (Klein 1999, 2000b). This tool industry is characterized by large hand axes and a variety of flake tools. There is no evidence of bows and arrows or spear throwers during this time, although wooden spears have been found (Thieme 1997). Acheulean stone tools commonly occur near animal bones on ancient land surfaces, but a functional relationship between them cannot be assumed. These sites are mainly open-air localities near ancient streams or ponds that would have naturally attracted humans and animals (Klein 2000b). The bones could represent human kills, or they could be natural deaths or carnivore kills that were either left alone or scavenged by other carnivores, including humans. For example, at the site of Duinefontein, South Africa, animal bones and stone tools accumulated around marshy dune swales 200,000–400,000 years ago (Klein et al. 1999). Giant buffalo (Pelorovis antiquus) from the site follows an attritional pattern with many old animals and only a few juveniles. Black wildebeest (Connochates gnou) also is represented by only a few juveniles, but many young adults (about 2 years old) also are present. Continuing excavations have increased the sample and confirmed these patterns (R. Klein, pers. comm.). Brown hyenas (Hyaena brunnea) do not hunt animals the size of black wildebeest, but carnivore marks greatly outnumber stone tool marks on all bones, making the cause of mortality inconclusive (Klein et al. 1999). Humans may have had Vol. 84, No. 2 little involvement with the animal remains; they could have hunted the animals, or they could have scavenged the remains of natural deaths or other carnivoran kills. Isolating the role of humans in Acheulean sites is difficult, and carnivore involvement in the form of chew marks and fossilized feces is often obvious (Gaudzinski and Turner 1996; Klein 2000b). Frequently, samples are too small to create informative mortality profiles. True occupation sites would be useful, such as those in caves, although such sites may not exist for this time period. However, the collective literature on Acheulean assemblages suggests that these early humans were unable to regularly hunt prime-age prey. Middle Stone Age (Africa) and Middle Paleolithic (Europe).—The Middle Stone Age followed the Acheulean in Africa spanning from 200,000–250,000 years ago to about 50,000 years ago and is associated with H. helmei, which is also referred to as archaic H. sapiens (Klein 1999, 2000a). The Middle Paleolithic followed the Acheulean in Europe, persisted until about 35,000 years ago, and is associated with H. neanderthalensis, the Neanderthals (Klein 1999, 2000a). The stone tool industries for these 2 groups are very similar and are also similar to flake tools found in Acheulean assemblages; there is no evidence of bows and arrows or spear throwers during this time (Klein 1999). It does appear that stone points were mounted onto wooden shafts, possibly to be used as thrusting spears (Shea 1989, 1998; Shea et al. 2001). Klasies River Mouth cave I, South Africa (74,000–128,000 years ago) provides an example of how an early human group hunted different species with different strategies (Klein 1978, 1994; Klein and CruzUribe 1996). Mortality profiles of Cape buffalo from this site reflect the idealized attritional profile (Fig. 3). The abundance of juveniles suggests that Middle Stone Age people hunted buffalo and did not scavenge off the natural attrition of the herd, because other carnivores are likely to consume ju- May 2003 SPECIAL FEATURE—MAMMALIAN PALEONTOLOGY 425 FIG. 3.—Mortality profiles of eland (Taurotragus oryx) and Cape buffalo (Syncerus caffer) from the Middle Stone Age site of Klasies River Mouth, South Africa. When hunting buffalo, Klasies people primarily took young and old (most vulnerable) individuals of this large and dangerous species. They were able to regularly hunt prime-age eland, potentially by driving them. Data from Klein (1994; drawings courtesy of R. Klein). venile carcasses quickly and completely, as is apparent in the wolf-kill sample presented here. Nonetheless, Klasies people were able to take only young and old individuals, presumably because buffaloes were large and dangerous and Middle Stone Age people lacked projectile technology. In contrast, eland (Taurotragus oryx) from this site produces a mortality profile that is very similar to the catastrophic model, indicating that early people were able to take individuals of all ages of this species. Klein et al. (1999) suggested that this relatively docile species was driven either over cliffs or into blind traps. Other Middle Stone Age sites in South Africa also show this pattern of age structure for eland (Klein and Cruz-Uribe 1984, 1996), and historic observations indicate that this species was amenable to driving (Klein and Cruz-Uribe 1991). This example shows how attributes of prey behavior (and other attributes such as body size) directly affect hunting strategies, so these attributes must always be considered when interpreting mortality profiles. Early humans from similar time periods and with similar tool technology may have used different strategies to hunt the same species. Paleolithic people in southwestern Europe frequently hunted red deer (Cervus elaphus) when it was available. Four Middle Paleolithic assemblages show variation in red deer age structures (Fig. 4). Lazaret (130,000–170,000 years ago) is from Nice, France (Valensi 1996), Combe-Grenal layers 1–35 and 36–54 (45,000–71,000 years ago and 71,000–115,000 years ago) are from Domme in southwestern France (Chase 1986; Delpech 1996; Mellars 1996), and Gabasa (about 46,000 years ago) is from Aragón near the Spanish Central Pyrenees (Blasco 1997). Preservation in the assemblages is comparable, and all are from modern archaeological excavations. I compare these samples with 4 Upper Paleolithic samples spanning 11,000–21,000 years ago that were accumulated by fully modern humans from northern Spain: El Castillo (Klein and Cruz-Uribe 1994; data provided by R. Klein), El Juyo (Freeman et al. 1988; data provided by R. Klein), Urtiaga (Altuna 1972), and La Riera (Straus and Clark 426 JOURNAL OF MAMMALOGY FIG. 4.—Mortality profiles of red deer (Cervus elaphus) from Middle and Upper Paleolithic sites in southwestern Europe. Histograms are complete age profiles, and box plots compare only adults. Methods for histogram and box-plot construction are the same as in Fig. 2. Box plots compare median m1 crown heights that were standardized by average unworn crown height for the sample to control for differences in body size of red deer (Steele 2002). Mortality profiles from Middle Paleolithic assemblages overlap with assemblages from Upper Paleolithic sites. Similar to modern humans, many Neanderthals harvested many prime-age red deer. Data from Steele (2002). 1986). Both samples from Combe-Grenal and the Lazaret sample show hunting of adult animals, whereas Gabasa has a high proportion of young. When only adults are considered in box plots, Gabasa’s median is not significantly different from Upper Paleolithic samples, and the Combe-Grenal and Lazaret samples fall within the range of prime-age animals. These profiles sug- Vol. 84, No. 2 gest that some groups of Middle Paleolithic hunters regularly took prime red deer, whereas other groups took mostly young adults. Other Middle Paleolithic sites show strong evidence that Neanderthals had the ability to regularly capture adult prey. Multiple sites ranging from 35,000 to 190,000 years ago in southern France, including La Borde, Mauran, and Coudoulous, contain large numbers (87–100%) of either steppe bison (Bison priscus) or auroch (Bos primigenius—Jaubert and Brugal 1990). Similar sites also are located in Germany and Russia (Gaudzinski 1996). Assemblages from each of these sites produced mortality profiles with high proportions of prime adult individuals (Brugal and David 1993; Slott-Moller 1990). The sites are all either open-air or in sink-hole–type features. Archaeological and ethnographic evidence of comparable species in North America suggests that these animals could have been driven, and either sink holes (Jaubert and Brugal 1990) or constructed barriers could have been used to trap animals. The site of Salzgitter Lebenstedt (54,000–58,000 years ago) in northern Germany also is dominated by adults of 1 species, reindeer (Rangifer tarandus—Gaudzinski and Roebroeks 2000). The authors concluded that the site indicates group kills, but the mortality profile shows an abundance of older adults; the actual mode of accumulation remains unclear. Examination of mortality profiles from several sites reveals that the ability to regularly hunt adults of some prey species emerged during the Middle Paleolithic of Europe and Middle Stone Age of Africa. This behavior apparently evolved in humans before other aspects of modern behavior appeared and before modern skeletal anatomy became globally distributed approximately 50,000 years ago (Klein 1999, 2000a). Exact modes of prey acquisition remain obscure, and it is unclear if these early hunters were taking individual prey in proportion to their abundance on the landscape, May 2003 SPECIAL FEATURE—MAMMALIAN PALEONTOLOGY driving entire herds (both would produce mortality profiles closer to the idealized catastrophic structure), or targeting prime-age individuals. FUTURE RESEARCH To understand the timing of changes in human hunting strategies, more comprehensive comparative analyses must be undertaken. Although only a few examples are presented here, mortality profiles during the Late Pleistocene show great variation. Future analyses should include data from nonhuman carnivores, so that more paleontological comparisons can be made between species. This also may allow the contexts of predation decisions to be investigated. As controls for archaeological studies, more paleontological accumulations are needed to understand better the pre- and postdepositional processes that affect skeletal remains from the time of death until excavation and to isolate the human component of archaeological assemblages better. The context of a fossil assemblage must always be considered, and results should be regarded with caution until a consistent pattern appears. Only in this comparative framework can behavior be reliably inferred from fossil assemblages. Mortality profiles of prey vary with the predator species, and therefore they provide a powerful tool for illuminating how predators select from prey populations. It is possible to use mortality profiles to track changes in predator behavior in the fossil record, including the evolution of various carnivore niches. In this study, I used mortality profiles to track human behavioral evolution and showed that the human ability to consistently harvest prime-age animals developed before the origins of fully modern humans. This conclusion is significant because it shows that starting well back into the Pleistocene, humans hunted differently from nonhuman predators, a conclusion made possible by the study of age distributions reconstructed from fossil assemblages. 427 ACKNOWLEDGMENTS I thank E. Hadly for inviting me to participate in this symposium. I. Aguilera and V. Baldellou (Huesca Musuem, Huesca, Spain), P. Utrilla and F. Blasco (Universidad de Zaragoza, Zaragoza, Spain), J. Altuna and K. Mariezkurrena (Sociedad de Ciencias Aranzadi, San Sebastián/Donostia, Spain), E. Tessier (Museo Arqueológico de Asturias, Oviedo, Spain), H. de Lumley, A. Echassoux, and P. Valensi (Laboratoire de Préhistoire du Lazaret, Nice, France), F. Delpech (Université Bordeaux I, Talence, France), K. Hamlin (Montana Department of Fish, Wildlife, and Parks, Bozeman), L. Irby (Montana State University, Bozeman), and J. Varley and D. Smith (Center for Resources, Yellowstone National Park, Wyoming) generously provided access to faunal material. I thank E. Hadly, R. Klein, T. Weaver, and 2 anonymous reviewers for their comments on an earlier draft and J. Rick for previous comments; R. Klein provided some data and the animal and tooth drawings. LITERATURE CITED ALTUNA, J. 1972. Fauna de mamı́feros de los yacimientos prehistóricos de Guipuzcoa. Munibe 24:1– 464. AMOROSI, T. 1989. A postcranial guide to domestic neo-natal and juvenile mammals. BAR international series. British Archaeological Reports, Oxford, United Kingdom 533:1–380. BARTRAM, L. E. 1993. Perspectives on skeletal part profiles and utility curves from eastern Kalahari ethnoarchaeology. Pp. 115–137 in From bones to behavior: ethnoarchaeological and experimental contributions to the interpretation of faunal remains (J. Hudson, ed.). Center for Archaeological Investigations, Southern Illinois University, Carbondale. BERGER, J., ET AL. 2001. Back-casting sociality in extinct species: new perspectives using mass death assemblages and sex ratios. Proceedings of the Royal Society of London, B. Biological Sciences 268:131– 139. BINFORD, L. R., AND J. B. BERTRAM. 1977. Bone frequencies and attritional processes. Pp. 77–153 in For theory building in archaeology (L. R. Binford, ed.). Academic Press, New York. BLASCO, M. F. 1997. In the pursuit of game: the Mousterian cave site of Gabasa I in the Spanish Pyrennes. Journal of Anthropological Research 53:177–217. BLEICH, V. C., R. T. BOWYER, AND J. D. WEHAUSEN. 1997. Sexual segregation in mountain sheep: resources or predation? Wildlife Monographs 134:1– 50. BLUMENSCHINE, R. J. 1987. Characteristics of an early hominid scavenging niche. Current Anthropology 28:383–407. BOWYER, R. T. 1984. Sexual segregation in southern mule deer. Journal of Mammalogy 65:410–417. 428 JOURNAL OF MAMMALOGY BOYD, D. K., R. R. REAM, D. H. PLETSCHER, AND M. W. FAIRCHILD. 1994. Prey taken by colonizing wolves and hunters in the Glacier National Park area. Journal of Wildlife Management 58:289–295. BROWN, W. A. B., AND N. G. CHAPMAN. 1991a. Age assessment of red deer (Cervus elaphus): from a scoring scheme based on radiographs of developing permanent molariform teeth. Journal of Zoology (London) 225:85–97. BROWN, W. A. B., AND N. G. CHAPMAN. 1991b. The dentition of red deer (Cervus elaphus): a scoring scheme to assess age from wear of the permanent molariform teeth. Journal of Zoology (London) 224: 519–536. BRUGAL, J.-P., AND F. DAVID. 1993. Usure dentaire, courbe de mortalité et ‘‘saisonnalité’’: les gisements du Paléolithique moyen à bovidés. Pp. 63–77 in Exploitation des animaux sauvages a travers le temps (J. Desse and F. Audoin-Rouzeau, eds.). Editions association pour la promotion et la diffusion des connaissances archéologiques, Juan-les-Pins, France. BUNN, H. T. 1993. Bone assemblage at base camps: a further consideration of carcass transport and bone destruction by the Hadza. Pp. 156–168 in From bones to behavior: ethnoarchaeological and experimental contributions to the interpretation of faunal remains (J. Hudson, ed.). Center for Archaeological Investigations, Southern Illinois University, Carbondale. CARBYN, L. N. 1983. Wolf predation on elk in Riding Mountain National Park, Manitoba. Journal of Wildlife Management 47:963–976. CAUGHLEY, G. 1966. Mortality patterns in mammals. Ecology 47:906–918. CAUGHLEY, G. 1977. Analysis of vertebrate populations. John Wiley & Sons, Inc., London, United Kingdom. CHASE, P. G. 1986. The hunters of Combe-Grenal: approaches to Middle Paleolithic subsistence in Europe. BAR international series. British Archaeological Reports, Oxford, United Kingdom 286:1–224. DEEVEY, E. S. 1947. Life tables for natural populations of animals. Quarterly Review of Biology 22:283– 314. DELPECH, F. 1996. L’environnement animal des Mousteriens Quina du Perigord. Paleo 8:31–46. D’ERRICO, F., AND M. VANHAEREN. 2002. Criteria for identifying red deer (Cervus elaphus) age and sex from their canines. Application to the study of Upper Palaeolithic and Mesolithic ornaments. Journal of Archaeological Science 29:211–232. DUCOS, P. 2000. A new approach to the construction of age profiles. ArchaeoZoologia 11:135–144. FLOOK, D. R. 1970. Causes and implications of an observed sex differential in the survival of wapiti. Canadian Wildlife Service Report Series 11:1–71. FREEMAN, L. G., J. GONZÁLEZ ECHEGARAY, R. G. KLEIN, AND W. T. CROWE. 1988. Dimensions of research at El Juyo. Pp. 3–39 in Upper Pleistocene prehistory of western Eurasia (H. L. Dibble and A. Montet-White, eds.). University Museum, Philadelphia, Pennsylvania. FRISON, G. C. 1978. Animal population studies and cultural inference. Plains Anthropologist 23:44–52. FRISON, G. C. 1991. Hunting strategies, prey behavior Vol. 84, No. 2 and mortality data. Pp. 15–30 in Human predators and prey mortality (M. C. Stiner, ed.). Westview Press, Boulder, Colorado. GASAWAY, W. C., R. D. BOERTJE, D. V. GRANGAARD, D. G. KELLEYHOUSE, R. O. STEPHENSON, AND D. G. LARSEN. 1992. The role of predation in limiting moose at low densities in Alaska and Yukon and implications for conservation. Wildlife Monographs 120:1–59. GASAWAY, W. C., R. O. STEPHENSON, J. L. DAVIS, P. E. K. SHEPHERD, AND O. BURRIS. 1983. Interrelationships of wolves, prey, and man in interior Alaska. Wildlife Monographs 84:1–50. GAUDZINSKI, S. 1996. On bovid assemblages and their consequences for the knowledge of subsistence patterns in the Middle Paleolithic. Proceedings of the Prehistoric Society 62:19–39. GAUDZINSKI, S., AND W. ROEBROEKS. 2000. Adults only. Reindeer hunting at the Middle Palaeolithic site Salzgitter Lebenstedt, northern Germany. Journal of Human Evolution 38:497–521. GAUDZINSKI, S., AND E. TURNER. 1996. The role of early humans in the accumulation of European Lower and Middle Palaeolithic bone assemblages. Current Anthropology 37:153–156. GEIST, V. 1982. Adaptive behavioral strategies. Pp. 219–277 in Elk of North America: ecology and management (J. W. Thomas and D. E. Toweill, eds.). Stackpole Books, Harrisburg, Pennsylvania. HADLY, E. A. 1999. Fidelity of terrestrial vertebrate fossils to a modern ecosystem. Palaeogeography, Palaeoclimatology, Palaeoecology 149:389–409. HAMLIN, K. L., D. F. PAC, C. A. SIME, R. M. DESIMONE, AND G. L. DUSEK. 2000. Evaluating the accuracy of ages obtained by two methods for Montana ungulates. Journal of Wildlife Management 64:441–449. HEWISON, A. J. M., J. P. VINCENT, J. M. ANGIBAULT, D. DELORME, G. VAN LAERE, AND J. M. GAILLARD. 1999. Tests of estimation of age from tooth wear on roe deer of known age: variation within and among populations. Canadian Journal of Zoology 77:58–67. HOUSTON, D. B. 1982. The northern Yellowstone elk: ecology and management. Macmillan Publishing Company, Inc., New York. JAUBERT, J., AND J.-P. BRUGAL. 1990. Contribution à l’étude du mode de vie au Paléolithique moyen: les chasseurs d’aurochs de la Borde. Pp. 128–145 in Les chasseurs d’aurochs de La Borde: un site du Paléolithique moyen (Livernon, Lot) (J. Jaubert, M. Lorblanchet, H. Laville, R. Slott-Moller, A. Turq, and J.-P. Brugal, eds.). Maison des Sciences de l’Homme, Paris, France (Documents d’Archéologie Française 27). KEISS, R. E. 1969. Comparison of eruption-wear patterns and cementum annuli as age criteria in elk. Journal of Wildlife Management 33:175–180. KIE, J. G., AND R. T. BOWYER. 1999. Sexual segregation in white-tailed deer: density-dependent changes in use of space, habitat selection, and dietary niche. Journal of Mammalogy 80:1004–1020. KIERDORF, U., AND J. BECHER. 1997. Mineralization and wear of mandibular first molars in red deer (Cervus elaphus) of known age. Journal of Zoology (London) 241:135–143. KLEIN, R. G. 1978. Stone Age predation on large Af- May 2003 SPECIAL FEATURE—MAMMALIAN PALEONTOLOGY rican bovids. Journal of Archaeological Science 5: 195–217. KLEIN, R. G. 1982. Patterns of ungulate mortality and ungulate mortality profiles from Langebaanweg (Early Pliocene) and Elandsfontein (Middle Pleistocene), south-western Cape Province, South Africa. Annals of the South African Museum 20:49–94. KLEIN, R. G. 1994. Southern Africa before the Iron Age. Pp. 471–519 in Integrative paths to the past: paleoanthropological advances in honor of F. Clark Howell (R. S. Corruccini and R. L. Ciochon, eds.). Prentice Hall, Inc., Englewood Cliffs, New Jersey. KLEIN, R. G. 1999. The human career: human biological and cultural origins. 2nd ed. University of Chicago Press, Chicago, Illinois. KLEIN, R. G. 2000a. Archaeology and the evolution of human behavior. Evolutionary Anthropology 9:17– 36. KLEIN, R. G. 2000b. The Earlier Stone Age of southern Africa. South African Archaeological Journal 55:1– 16. KLEIN, R. G., K. ALLWARDEN, AND C. WOLF. 1983. The calculation and interpretation of ungulate age profiles from dental crown heights. Pp. 47–57 in Hunter-gatherer economy in prehistory: a European perspective (G. Bailey, ed.). Cambridge University Press, Cambridge, United Kingdom. KLEIN, R. G., ET AL. 1999. Duinefontein 2: an Acheulean site in the Western Cape Province of South Africa. Journal of Human Evolution 37:153–190. KLEIN, R. G., AND K. CRUZ-URIBE. 1984. The analysis of animal bones from archeological sites. University of Chicago Press, Chicago, Illinois. KLEIN, R. G., AND K. CRUZ-URIBE. 1991. The bovids from Elandsfontein, South Africa, and their implications for the age, palaeoenvironment, and origins of the site. African Archaeological Review 9:21–79. KLEIN, R. G., AND K. CRUZ-URIBE. 1994. The Paleolithic mammalian fauna from the 1.910-14 excavations at El Castillo Cave (Cantabria). Museo y Centro de Investigación de Altamira 17:141–158. KLEIN, R. G., AND K. CRUZ-URIBE. 1996. Exploitation of large bovids and seals at Middle and Later Stone Age sites in South Africa. Journal of Human Evolution 31:315–334. KNIGHT, R. R., B. BLANCHARD, AND P. SCHULLERY. 1999. Yellowstone bears. Pp. 51–75 in Carnivores in ecosystems: the Yellowstone experience (T. W. Clark, A. P. Curlee, S. C. Minta, and P. M. Kareiva, eds.). Yale University Press, New Haven, Connecticut. KOIKE, H., AND N. OHTAISHI. 1985. Prehistoric hunting pressure estimated by the age composition of excavated sika deer (Cervus nippon) using the annual layer of tooth cement. Journal of Archaeological Science 12:443–456. KUNKEL, K. E., T. K. RUTH, D. H. PLETSCHER, AND M. G. HORNOCKER. 1999. Winter prey selection by wolves and cougars in and near Glacier National Park, Montana. Journal of Wildlife Management 63: 901–910. KURTÉN, B. 1953. On the variation and population dynamics of fossil and recent mammal populations. Acta Zoologica Fennica 76:1–122. LEVINE, M. A. 1983. Mortality models and the inter- 429 pretation of horse population structure. Pp. 23–46 in Hunter-gatherer economy in prehistory: a European perspective (G. Bailey, ed.). Cambridge University Press, Cambridge, United Kingdom. LOWE, V. P. W. 1967. Teeth as indicators of age with special reference to red deer (Cervus elaphus) of known age from Rhum. Journal of Zoology (London) 152:137–153. LUBINSKI, P. M. 2001. Observations on seasonality and mortality from a recent catastrophic death assemblages. Journal of Archaeological Science 28:833– 842. LYMAN, R. L. 1994. Vertebrate taphonomy. Cambridge University Press, Cambridge, United Kingdom. MAREAN, C. W. 1997. Hunter-gatherer foraging strategies in tropical grasslands: model building and testing in the East African Middle and Later Stone Age. Journal of Anthropological Archaeology 16:189– 225. MCCABE, R. E. 1982. Elk and Indians: historical values and perspectives. Pp. 61–123 in Elk of North America: ecology and management (J. W. Thomas and D. E. Toweill, eds.). Stackpole Books, Harrisburg, Pennsylvania. MCCULLOUGH, D. R. 1979. The George Reserve deer herd: population ecology of a K-selected species. University of Michigan Press, Ann Arbor. MECH, L. D., D. W. SMITH, K. M. MURPHY, AND D. R. MACNULTY. 2001. Winter severity and wolf predation on a formerly wolf-free elk herd. Journal of Wildlife Management 65:998–1003. MELLARS, P. 1996. The Neanderthal legacy. Princeton University Press, Princeton, New Jersey. MITCHELL, B. 1967. Growth layers in dental cement for determining the age of red deer (Cervus elaphus L.). Journal of Animal Ecology 36:279–293. MORRIS, P. 1972. A review of mammalian age determination methods. Mammal Review 2:69–104. MORRISON, D., AND P. WHITRIDGE. 1997. Estimating the age and sex of caribou from mandibular measurements. Journal of Archaeological Science 24:1093– 1106. MUNSON, P. J. 1991. Mortality profiles of white-tailed deer from archaeological sites in eastern North America: selective hunting or taphonomy? Pp. 139– 151 in Beamers, bobwhites, and blue-points: tributes to the career of Paul W. Parmalee (J. R. Purdue, W. E. Klippel, and B. W. Styles, eds.). Illinois State Museum Scientific Papers, Springfield. MUNSON, P. J. 2000. Age-correlated differential destruction of bones and its effect on archaeological mortality profiles of domestic sheep and goat. Journal of Archaeological Science 27:391–407. NIMMO, B. W. 1971. Population dynamics of a Wyoming pronghorn cohort from the Eden-Farson site, 48SW304. Plains Anthropologist 16:285–288. O’CONNOR, T. 2000. The archaeology of animal bones. Texas A&M University Press, College Station. PIKE-TAY, A. 1991. Red deer hunting in the Upper Paleolithic of south-west France: a study in seasonality. BAR international series. British Archaeological Reports, Oxford, United Kingdom 569:1–183. PIKE-TAY, A. 2000. Innovations in assessing season of capture, age and sex of archaeofaunas. ArchaeoZoologia 11:1–238. 430 JOURNAL OF MAMMALOGY PIKE-TAY, A., C. A. MORCOMB, AND M. O’FARRELL. 2000. Reconsidering the quadratic crown height method of age estimation for Rangifer from archaeological sites. ArchaeoZoologia 11:145–174. PITTS, M. 1979. Hides and antlers: a new look at the gatherer-hunter site at Star Carr, North Yorkshire, United Kingdom. World Archaeology 2:32–42. QUIMBY, D. C., AND J. E. GAAB. 1957. Mandibular dentition as an age indicator in Rocky Mountain elk. Journal of Wildlife Management 21:435–451. REITZ, E. J., AND E. S. WING. 1999. Zooarchaeology. Cambridge University Press, Cambridge, United Kingdom. SHEA, J. J. 1989. A functional study of the lithic industries associated with hominid fossils in the Kebara and Qafzeh caves, Israel. Pp. 611–625 in The human revolution: behavioural and biological perspectives on the origins of modern humans (P. Mellars and C. B. Stringer, eds.). Edinburgh University Press, Edinburgh, United Kingdom. SHEA, J. J. 1998. Neanderthal and early modern human behavioral variability. Current Anthropology 39: S45–S78. SHEA, J. J., Z. DAVIS, AND K. BROWN. 2001. Experimental tests of Middle Palaeolithic spear points using a calibrated crossbow. Journal of Archaeological Science 28:807–816. SINGER, F. J., AND J. A. MACK. 1999. Predicting the effects of wildfire and carnivore predation on ungulates. Pp. 189–237 in Carnivores in ecosystems: the Yellowstone experience (T. W. Clark, A. P. Curlee, S. C. Minta, and P. M. Kareiva, eds.). Yale University Press, New Haven, Connecticut. SKOGLAND, T. 1988. Tooth wear by food limitation and its life history consequences in wold reindeer. Oikos 51:238–242. SLOTT-MOLLER, R. 1990. La faune. Pp. 33–68 in Les chasseurs d’aurochs de La Borde: un site du Paléolithique moyen (Livernon, Lot) (J. Jaubert, M. Lorblanchet, H. Laville, R. Slott-Moller, A. Turq, and J.-P. Brugal, eds.). Maison des Sciences de l’Homme, Paris, France (Documents d’Archéologie Française 27). SMITH, D. W., W. G. BREWSTER, AND E. E. BANGS. 1999. Wolves in the Greater Yellowstone ecosystem: restoration of a top carnivore in a complex management environment. Pp. 103–125 in Carnivores in ecosystems: the Yellowstone experience (T. W. Clark, A. P. Curlee, S. C. Minta, and P. M. Kareiva, eds.). Yale University Press, New Haven, Connecticut. Vol. 84, No. 2 SOKAL, R. R., AND F. J. ROHLF. 1995. Biometry: the principles and practice of statistics in biological research. 3rd ed. W. H. Freeman and Company, New York. SPINAGE, C. A. 1972. Age estimation of zebra. East African Wildlife Journal 10:273–277. SPINAGE, C. A. 1973. A review of age determination of mammals by means of teeth, with special reference to Africa. East African Wildlife Journal 11: 165–187. STEELE, T. E. 2002. Red deer: their ecology and how they were hunted by Late Pleistocene hominids in western Europe. Ph.D. dissertation, Stanford University, Stanford, California. STEPHENS, D. W., AND J. R. KREBS. 1986. Foraging theory. Princeton University Press, Princeton, New Jersey. STINER, M. C. 1990. The use of mortality patterns in archaeological studies of hominid predatory adaptations. Journal of Anthropological Archaeology 9: 305–351. STRAUS, L. G., AND G. A. CLARK. 1986. La Riera Cave: stone age hunter-gatherer adaptations in northern Spain. Anthropological research papers. Arizona State University, Tempe. THIEME, H. 1997. Lower Palaeolithic hunting spears from Germany. Nature 385:807–810. VALENSI, P. 1996. Taphonomie des grands mammifères et palethnologies à la Grotte du Lazaret (Nice, France). Anthropozoologica 23:13–28. VAN BALLENBERGHE, V., AND W. B. BALLARD. 1997. Population dynamics. Pp. 223–245 in Ecology and management of the North American moose (A. W. Franzmann and C. C. Schwartz, eds.). Smithsonian Institution Press, Washington, D.C. VAN DEELEN, T. R., K. M. HOLLIS, C. ANCHOR, AND D. R. ETTER. 2000. Sex affects age determination and wear of molariform teeth in white-tailed deer. Journal of Wildlife Management 64:1076–1083. VAN VALEN, L. 1964. Age in two fossil horse populations. Acta Zoologica 45:93–106. VOORHIES, M. R. 1969. Taphonomy and population dynamics of an early Pliocene vertebrate fauna, Knox County, Nebraska. University of Wyoming, Laramie 1:1–69. WILSON, B., C. GRIGSON, AND S. PAYNE. 1982. Ageing and sexing animal bones from archaeological sites. BAR British series. British Archaeological Reports, Oxford United Kingdom 109:1–268. Special Feature Editor was D. M. Leslie, Jr.