© Springer International Publishing AG, part of Springer Nature 2018
Diane Gifford-GonzalezAn Introduction to Zooarchaeologyhttps://doi.org/10.1007/978-3-319-65682-3_21

21. Calibrating Bone Durability

Diane Gifford-Gonzalez1 
(1)
Department of Anthropology, University of California, Santa Cruz, CA, USA
 

Keywords

TaphonomyPreservationAttritionPhoton densitometerCTscanBMD

While some zooarchaeologists worked to standardize the nutritional values of tissues associated with various skeletal elements , others raised a second, intersecting issue: the role of differential element durability in determining element frequencies in archaeofaunal assemblages. The paleontological taphonomic literature has long distinguished two types of postmortem processes that produce element frequencies in fossil accumulations: transport of elements away from or to a sample locale, on the one hand and in situ, or in-place, destruction of elements at the locality, on the other Guthrie (1967; Lawrence 1968; Olson 1971). Paleontologists also recognized that skeletal elements vary in their construction and their densities of bone tissue and, therefore, in their potential for surviving postmortem taphonomic processes. Awareness of this literature led some zooarchaeologists to question whether archaeofaunal element frequencies were caused solely by human selective transport or whether durability-dependent deletion of more delicate skeletal elements could also affect them. This chapter reviews zooarchaeologists’ attempts to calibrate density-dependent bone attrition , and to assess how this relates to the effects of human selectivity.

In zooarchaeology , the potentially equifinal results of human selectivity and differential bone survival have generated a profusion of studies and controversies. This literature is complicated in several ways. First, many such discussions implicate multiple, variable, and often-unarticulated base assumptions about how to link actualistic research to archaeofaunal case analyses. Second, some methodological discussions concerning bone tissue density are offered in the context of arguments over methods of quantification ; these are indeed related topics, but teasing out the strands of one from the other is challenging. Third, these discussions are often entangled with competing claims regarding early hominin behavior, with which the average zooarchaeological reader may neither be thoroughly acquainted nor deeply concerned. All participants in these sometimes heated debates believe they are doing good science, the logic of opposed lines of argument is close to impeccable, and it only becomes more so with time – but the same is true for many theological positions. The reader interested in how best to assess in situ destruction cannot be faulted for becoming dazed around the thirtieth article.

The first part of this chapter aims to sort through basic themes in research on bone durability in zooarchaeology since the 1980s, abstracting them from the topically based arguments in which many are embedded. It accepts a priori that element frequencies should be seen as potentially subject to equifinality : like stone striations on bone surfaces, multiple processes and actors can caused them. Moreover, some authors remind us that element frequencies are abstracted statistics based upon NISP and that the chain of analytic procedures can, if care is not taken, determine the final pattern of the aggregate data (Rogers 2000). The second part of this chapter examines quantitative issues associated with element survival in more detail.

21.1 Fundamental Questions in Durability-Related Survival of Skeletal Elements

It is useful to outline relevant, intersecting issues relating to skeletal element durability in the form of questions, to be discussed in this section of the chapter.
  1. 1.

    Do various skeletal elements have different amounts of bone tissue per unit volume?

     
  2. 2.
    Can this variability be calibrated with a degree of replicability?
    1. (a)

      What factors can throw off estimates? Can they be corrected for?

       
    2. (b)

      What method is currently most accurate in estimating bone mineral density ? Why?

       
     
  3. 3.

    Does a negative correlation exist between nutritional utility and bone durability? That is, are the skeletal elements most likely to be selected for transport also the most fragile and vulnerable to destruction?

     
  4. 4.
    What causes destruction of more fragile elements or portions of elements?
    1. (a)

      Can we tell which actor or other taphonomic process is involved?

       
     
  5. 5.
    How can we apply knowledge of bone durability to archaeofaunal analysis?
    1. (a)

      How can one distinguish in situ destruction from selective transport ?

       
    2. (b)

      How can one best assess skeletal element representation?

       
     

The next subsections take these topics in turn, reviewing zooarchaeological research on the role of bone durability as a structuring factor in producing archaeofaunal element frequencies . It reviews the basic analytical methods developed to assess and compare density-dependent bone destruction, with some key references to the current state of knowledge and opinion. Recall that this chapter, like Chap. 20, focuses on aggregate patterning of element frequencies . These are believed to shed light on recurrent patterns of human behavior or its social and ecological contexts, as represented by the nested boxes for levels of inference introduced in Chap. 3. The continued relevance of drawing upon actor/effector evidence to assist in skeletal elements will be stressed.

21.1.1 Do Skeletal Elements Differ in Their Amounts of Bone Tissue per Unit Volume?

A casual observer handling a disarticulated skeleton laid out on a tabletop intuitively grasps that not all skeletal parts contain the same amount of bone tissue in relation to their overall size. The sternum and sacrum are very light, being composed nearly entirely of cancellous tissue with a thin veneer of cortical bone , while carpals and tarsals are much heavier due to their much denser compact bone tissue. As was the case with bone fracture patterns, properties inherent to the elements themselves, rather than the modifying actors , can strongly influence element survival in the face of destructive processes, and thereby structure element frequencies . Human selectivity may produce the initial element frequencies in an assemblage, but actualistic research in paleontology and zooarchaeology has shown that subsequent mechanical or chemical forces can modify these original frequencies according to different elements’ intrinsic properties, including their surface area in relation to their volume, as it did with weathering and the amount of bone tissue per unit volume.

21.1.2 Can this Variability be Measured with a Degree of Replicability?

As part of his palaeoanthropological research on differential skeletal element survival (Chap. 2), Brain (see 1981 for an overview) measured modern goat elements’ specific gravity, using the time-honored water-displacement method. He noted that the differences in modern element survival rates when subjected to carnivore gnawing or ungulate trampling correlated well with this measure. Behrensmeyer (1975) also recorded observations on the specific gravities of skeletal elements from modern taxa analogous to those found in fossil deposits in the Lake Turkana basin. Binford and Bertram (1977) attempted to extend Brain ’s use of specific gravity to their study of skeletal element destruction by Alaskan working dogs and wolves, but found the method wanting as a readily replicable process. Thus, by the early 1980s, paleontologists and zooarchaeologists were increasingly concerned with how best to distinguish selective transport of body segments from differential destruction by various agents, especially carnivores . Some sought more readily replicated methods for assessing the bone tissue density of various skeletal elements .

Lyman (1984) observed that mammalian bone tissue has a single specific gravity and physical density, but that individual skeletal elements , with their differing combinations of compact and cancellous tissue, as well as their internal voids for marrow , comprise variable volumes of such tissue, with different resulting “volume densities.” Lyman (1984: Table 1) reviewed previous specific gravity studies, observing a wide variation in values produced for similar elements. He argued that variations in the bone tissue composition of skeletal elements , and hence their survival potentials, seriously complicate inferences about human behavior from archaeofaunal element frequencies and Binford ’s utility indices.

Lyman (1984) introduced a new level of replicability in estimating bone tissue density with the application of biomedical scanning equipment, specifically single-beam photon densitometry, to measure bone tissue in skeletal elements . At that time, photon absorptiometry was widely applied in measuring the bone tissue in patients at risk of osteoporosis, based on a representative element, usually the distal radius and ulna of the forearm. The single photon (“X-ray”) beam moves over a plate on which the scanned tissue rests. A detector on the plate registers the beam, with the tissue of the scanned tissue partially impeding the beam.

Because the photo beam sensor registers a two-dimensional scan line across the element, the volume of the bone tissue in a three-dimensional element must be estimated with a formula that converts the photon-derived reading into a three-dimensional figure. Lyman originally estimated bone volume at each scan site as the product of the beam scan’s width (1/8 in.), the maximum bone length, and the maximum bone thickness. Later, he used an average bone thickness (Lyman et al. 1992). The method treats all skeletal elements as cross-sectionally rectangular at the scan site and assumes that the element is a solid, lacking medullary or inter-trabecular spaces. These assumptions may not be warranted, as will be seen below. Nonetheless, Lyman ’s scan-site approach has guided later research and development on this topic.

Lyman initially called the resultant measure of bone tissue in three dimensions “bulk density,” which he defined as, “the ratio of the weight of a volume of a substance to the volume of that substance including the pore space volume” (1985: 226). Thus, the statistic should reflect the degree to which an element is tightly packed with bone tissue. By this criterion, vertebrae have low bulk density, and carpal and tarsal bones have very high bulk density. Later, Lyman (e.g. 1992) changed to the term “volume density” (VD ) as the more accurate name for the same index.

Lyman (1984) scanned multiple sites (Fig. 21.1) on axial and appendicular skeletal elements of 13 deer (Odocoileus virginianus and O. hemionus), plus a sheep (Ovis aries) and pronghorn antelope Antilocapra americana. He targeted scans to locations of Binford ’s MGUI values, such as the proximal and distal femur, adding long bone shafts, for which Binford had not assigned MGUI . He also made multiple scans for elements treated in aggregate by Binford , for example vertebral regions, ribs, carpals, and tarsals, but later averaged these values to compare with the MGUI . For any element to which Binford had given distinct (e.g. proximal and distal) MGUI values, he retained distinct values (Table 21.1).
images/324980_1_En_21_Chapter/324980_1_En_21_Fig1_HTML.gif
Fig. 21.1

Lyman’s scan sites (Lyman 1985: 274–275, Fig. 2), also used as the basis for CTscan sites by Lam et al. (1998, 1999). (Redrawn by the author, used with permission of R. L. Lyman and Elsevier)

Table 21.1

Summary of Lyman's (1985) scan sites for deer skeletal elements, with Volume Density (VD) values, and Lam et al.'s (1998) caribou CTScan Bone Mineral Density (BMD) values, according to their BMD1 and BMD2 calculations (see text for details)

Element

N

Lyman (1985) deer VD

Lam et al. (1998) Caribou CTScan

   

BMD1

BMD2

Cranium (petrosal)

1

N/S

 

1.29

Mandible

2

     

DN1

 

0.55

0.65

 

DN2

 

0.57

0.75

1.05

DN3

 

0.55

0.63

1.07

DN4

 

0.57

0.67

1.06

DN5

 

0.57

0.56

1.05

DN6

 

0.31

0.66

0.84

DN7

 

0.36

0.98

1.01

DN8

 

0.61

0.99

 

Atlas

1

     

AT1

 

0.13

0.47

 

AT2

 

0.15

0.42

 

AT3

 

0.26

0.49

 

Axis

1

     

AX1

 

0.16

0.62

 

AX2

 

0.10

0.42

 

AX3

 

0.16

0.42

 

Cervical

5

     

CE1

 

0.19

0.45

 

CE2

 

0.15

0.43

 

Thoracic

13

     

TH1

 

0.24

0.38

 

TH2

 

0.27

0.53

 

Lumbar

6

     

LU1

 

0.29

0.49

 

LU2

 

0.30

0.45

 

LU3

 

0.29

0.51

 

Sacrum

1

     

SC1

 

0.19

0.37

 

SC2

 

0.16

0.40

 

Innominate

2

     

IL1

 

0.20

0.43

 

IL2

 

0.49

0.70

1.02

AC1

 

0.27

0.64

 

PU1

 

0.46

0.58

 

PU2

 

0.24

0.54

 

IS1

 

0.41

0.67

0.94

IS2

 

0.16

0.30

 

Rib

26

     

RI1

 

0.26

0.47

 

RI2

 

0.25

0.49

 

RI3

 

0.40

0.62

0.96

RI4

 

0.24

0.65

0.94

RI5

 

0.14

0.40

0.40

Sternum

6

     

ST1

 

0.22

N/S

 

Scapula

2

     

SP1

 

0.36

0.66

1.01

SP2

 

0.49

0.73

1.04

SP3

 

0.23

0.73

 

SP4

 

0.34

0.69

1.01

SP5

 

0.28

0.48

 

P Humerus

2

     

HU1

 

0.24

0.26

 

HU2

 

0.25

0.31

0.44

Sh Humerus

       

HU3

 

0.53

0.61

1.12

D Humerus

       

HU4

 

0.63

0.62

1.08

HU5

 

0.39

0.48

 

P Radius

2

     

RA1

 

0.42

0.53

 

RA2

 

0.62

0.57

1.08

Sh Radius

       

RA3

 

0.68

0.73

1.09

D Radius

2

     

RA4

 

0.38

0.38

0.97

RA5

 

0.43

0.49

 

P Ulna

2

     

UL1

 

0.30

0.49

 

UL2

 

0.45

68

0.84

D Ulna

2

     

UL3

 

0.44

NS

NS

P Metacarpal

2

     

MC1

 

0.56

0.63

0.92

MC2

 

0.69

0.69

1.08

Sh Metacarpal

       

MC3

 

0.72

0.79

1.10

D Metacarpal

2

     

MC4

 

0.58

0.59

1.01

MC5

 

0.49

0.48

 

MC6

 

51

0.68

 

P Femur

2

     

FE1

 

0.41

0.39

 

FE2

 

0.36

0.35

. 52

FE3

 

0.33

0.35

0.74

Sh Femur

       

FE4

 

0.57

0.57

1.15

D Femur

       

FE5

 

0.37

0.40

0.61

FE6

 

0.28

0.32

 

FE7

 

N/S

0.30

 

Patella

2

     

PA1

 

0.31

0.57

 

P Tibia

2

     

TI1

 

0.30

0.35

 

TI2

 

0.32

0.44

1.01

Sh Tibia

       

TI3

 

0.74

0.71

1.13

D Tibia

2

     

TI4

 

0.51

0.53

1.12

TI5

 

0.50

0.39

0.73

Fibular

2

0.52

0.68

 

Naviculocuboid

2

     

NC1

 

0.39

0.56

 

NC2

 

0.33

0.62

 

NC3

 

0.62

0.55

 

Astragalus

2

     

AS1

 

0.47

0.68

 

AS2

 

0.59

0.70

 

AS3

 

0.61

0.63

 

Calcaneus

2

     

CA1

 

0.41

0.52

 

CA2

 

0.64

0.80

0.94

CA3

 

0.57

0.66

 

CA4

 

0.33

0.73

 

P Metatarsal

       

MR1

 

0.55

0.58

0.90

MR2

 

0.65

0.57

1.10

Sh Metatarsal

       

MR3

 

0.74

0.65

1.08

D Metatarsal

2

     

MR4

 

0.57

0.54

1.08

MR5

 

0.46

0.41

 

MR6

 

0.50

0.59

 

Phalanx 1

8

 

0.56

 

P11

 

0.36

0.48

 

P12

 

0.42

0.56

0.92

P13

 

0.57

0.71

 

Phalanx 2

8

     

P21

 

0.28

0.49

0.61

P22

 

0.25

0.64

0.72

P23

 

0.35

NS

 

Phalanx 3

8

     

P31

 

0.25

0.48

 

Carpals

10

     

Scaphoid

2

0.98

0.70

 

Lunate

2

0.83

0.67

 

Cuneiform

2

0.72

0.71

 

Magnum

2

0.74

0.69

 

Unciform

2

0.78

0.72

 

Over the next decade, a variety of VD estimation studies, using either single-beam photon or Dual-energy X-ray Absorptiometry (DEXA) scans, were made with skeletal elements of other taxa. These included the marmot Marmota marmota (Lyman et al. 1992), the leporids: domestic rabbit Oryctolagus cuniculus, eastern cottontail Sylvilagus floridanus, arctic hare Lepus canadensis, black-tailed jackrabbit Lepus californicus (Pavao and Stahl 1999), the bison Bison bison (Kreutzer 1992), the South American camelids: guanaco Lama guancoe, vicuña Lama vicugna, llama Lama glama, and alpaca Lama pacos (Elkin 1995; Stahl 1999), domestic cattle Bos taurus, domestic sheep Ovis aries, farmed European wild boar Sus scrofa (Ioannidou 2003), the turkey Meleagris gallopavo (Dirrigl 2001), the flightless lesser rhea Pterocnemia pennata (Cruz and Elkin 2003), and the North American harbor seal Phoca vitulina, with partial skeletons of the harp seal Phoca groenlandica included (Chambers in Lyman 1994: Table 7.7).

These findings were applied to assessing bone density-dependent bone destruction in various archaeological cases using rank-order correlation coefficient analysis. Lyman himself (1984, 1985) assessed several archaeofaunas purported to reflect selective transport , such as the Gatecliff Shelter , using volume density figures, as well as extending arguments about the relationship between nutritional utility and bone volume density, which will be treated in a subsequent sections.

21.1.2.1 Factors that Throw off Photon Densitometer Estimates: Bone Shape, Internal Voids

By the early 1990s, several researchers independently noted problems with the derivation of VD estimates in densitometry studies. Two issues emerged: first, the impact of variations in element shape on the realism of the VD estimate and second, the failure of the original formula to allow for an element’s internal voids in the estimate. In a study of human long bone volume density and survival, Galloway et al. (1996) explored how bone shape affects photon densitometer-derived VD estimates. They computed three estimates of bone mineral density : (1) the equipment-generated, non-shape-corrected estimate of gm/cm3, called BMD ; (2) Lyman ’s VD calculation, which divides that density estimate of an element by its thickness; (3) an estimate, which they called BMDc, that attempts to correct for differences in long bone cross-sectional shape by dividing the BMD “by a diameter calculated from the measured circumference” of an element (Galloway et al. 1996: 300), obtained by using a flexible tape to measure the long-bone circumference at a scan site, divided by 3.14 (pi). Using elements of different cross-sectional shapes, they demonstrated that the common VD formula assumptions produce considerable over-estimation of volume density (>125%) in elements with irregular cross-sectional shape. This problem was also recognized and explored by Pavao and Stahl (1999), who advocated VD estimation formulae that take into account the cross-sectional geometry of different leporid elements. See also Lyman ’s (2014) reworking of these data.

Regarding internal voids, Kreutzer (1992: 283) observed, that, using photon densitometry, there is:

…no way to account for the size of marrow cavities within long-bone shafts without sectioning the bones and measuring the cavities directly. Ideally, this would be done so that the dimensions of the marrow cavity within each scan site could be eliminated from the calculations of volume.

Kreutzer noted that this measurement is not feasible with museum comparative specimens , and she offers the opinion that both her own and Lyman ’s VD estimates for long-bone diaphyses are too low by an indeterminable amount. Elkin (1995) actually sectioned guanaco long bones to estimate bone wall BMD , having recognized that internal voids could throw off VD estimates (see also Cruz and Elkin 2003). Elkin (1995) also experimentally established that water-displacement estimates of bone VD produce substantially higher estimates of BMD than those produced by photon densitometry.

Lam and Pearson (2004, 2005) summarized four X-ray scanning technology approaches for estimating bone mineral density , which they classified according to their accuracy . The first were the simple, non-shape-corrected photon densitometer findings, they believe to be the least likely to produce an accurate bone mineral estimate for long bones with medullary cavities or irregularly shaped epiphyseal ends. The second comprise shape-corrected photon densitometer estimates such as those discussed by Galloway et al. (1996), which, however, do not estimate the size of and shape of medullary spaces. These, they say, produce better estimates but still yield values that depart in unpredictable ways from those produced by CTscan (see below), which does visualize internal voids (Lam and Pearson 2005:102, Fig. 1). The third variant, is also based on photon densitometry but also sections bone and uses estimates of medullary cavity size to produce render even more accurate BMD estimates, as did Elkin’s 1995 study. Fourth, Lam and Pearson (2004, 2005) contended that X-ray Computed Tomography scanning, commonly known as CTscans, render three-dimensional images of long-bone medullary cavities and cancellous bone tissue, using algorithms to calculate the three-dimensional bone mineral volume of an element. Lam and Pearson argue that CTscans produce the most accurate estimate of the bone mineral density .

21.1.2.2 Most Accurate Estimator of Bone Mineral Density: X-Ray Computed Tomography

Over several years, Lam and colleagues extensively explored the sources of error in photon densitometry estimates outlined above and developed CTscan applications to zooarchaeology (Lam et al. 1998, 1999, 2003; Lam and Pearson 2004, 2005). Computed Tomography scanning is used in medicine to produce three-dimensional images of soft and hard internal tissues of the body. The technique resembles photon densitometry in that an X-ray beam passes through a body or body segment to a beam receptor, with calibrations for impedance of the beam. However, CTscans employ digital processing software to interpolate three-dimensional images from multiple, two-dimensional “slices,” or scans, taken around a single axis of rotation.

For estimating bone mineral density , CTscans can represent both the actual external shape of a scanned skeletal element and the shapes and sizes of any internal voids, thus effectively addressing the two problems of photon densitometry scans (Fig. 21.2). The attenuation or impedance of the X-ray beam is expressed in “CT numbers” or Hounsfield units (Lam et al. 1998: 561), reflecting the calcium mineral densities within the scanned elements. A clinical product that permits calibration of bone mineral density (BMD), a solution of dipotassium phosphate, is scanned along with the bone specimens as baselines for imaging attenuation (Lam et al. 1998: 562). The bone mineral density, BMD (gm/cm3) is derived from the three-dimensional imaging.
images/324980_1_En_21_Chapter/324980_1_En_21_Fig2_HTML.gif
Fig. 21.2

Lam et al.’s (2003) illustration of problems with the photon densitometer correction factor approach, showing the imperviousness of the measure to overall bone shape and the presence, absence, and nature of internal voids. (From Lam et al. (2003: 1703, Fig. 1), used with permission of senior author and Elsevier)

Lam and colleagues (1998) initially produced bone BMD estimates for elements of goat (Capra hircus), using the same scan sites illustrated by Lyman , and compared their BMD results with Lyman’s cervid VD estimates. Notwithstanding taxonomic difference among these ruminant species, the values were highly correlated. Because some debate existed over whether density indices are ordinal, they offered both linear regression analysis (R 2 = 0.47, F = 27.80, P < 0·0001) and Pearson’s rho rank order correlation coefficient (r s = 0.68, P < 0·0001) between BMD and VD . However, Lam et al. stressed that the correlation masks the fact that CT BMD values for some element portions diverged markedly and importantly from those of photon densitometry VD for the same sites. For example, the femoral mid-shaft is the highest-ranked in BMD in CTscans, whereas it ranks seventeenth in VD calculations, results also suggested by Elkin’s 1995 study. Significantly for studying density-mediated attrition , CTscan BMD values for long-bone epiphyses display strong and consistent differences from diaphyses of the same elements that were not displayed in VD values for the same scan sites (Lam et al. 1998: 564). Applying both indices to caprine bones in two Southwest Asian archaeofaunas for which based on other criteria, they expected substantial carnivore attrition , they found that the CTscan BMD values correlated more strongly with log %MAU than did non-shape-corrected photon densitometer VD values (Table 21.2). Lam and co-workers attributed this to the greater realism of CTscans in estimating the actual amount of bone tissue in an element.
Table 21.2

Lam et al.’s (1998: 567, Table 3) regression and Spearman’s rho statistics for the relationships between the log %MAU in the two archaeological assemblages, Kobeh Cave and ‘Ain Dara Mound and the bone mineral density values using CTscan-based BMD estimates and photo densitometer based Volume Density (VD) estimates

 

Regression statistics

Spearman’s statistics

 

R 2

F

P

r s

P

Kobeh log %MAU by CT

0.56

37.08

<0.0001

0.5

<0.0001

Kobeh log %MAU by VD

0.18

6.30

0.0181

0.40

 0·0298

’Ain Dara log %MAU by CT

0.53

31.77

<0.0001

0.69

<0.0001

’Ain Dara log %MAU by VD

0.16

5.25

0.0296

0.40

0.0447

Lam et al. (1999) published BMD indices for reindeer/caribou Rangifer tarandus, a cervid, wildebeest Connochaetes taurinus, an African bovid, common zebra Equus quagga burchelli, and wild horse E. przewalskii. They used the same scan sites as Lyman ’s, and sometimes altered sites to adjust to osteological differences between ruminants and equids, and they added some elements such as the petrous temporal. The article details how two calculations were used to estimate BMD, depending upon whether the external cross-sectional outline at scan sites was sufficient for calculating the bone area (BMD1) or whether internal cross-section of medullary space must be traced to take into account the size and shape of the void within the element (BMD2).

Lam and colleagues (1999) compared BMD values among all taxa in their samples, plus Lyman’s deer and sheep and Elkin’s guanaco, the latter three being VD values (Table 21.1). They found that, especially among the ruminant artiodactyls, element BMD values were usually highly significantly correlated (p = <0.001). However, true to Kreutzer’s (1992) functional anatomical predictions, modest differences are found in such regions as the anterior cervicals, where differences in types of male-male competition probably have favored deposition of more or less bone mineral. The authors recommended that these extant BMD estimates are sufficient for application to most other taxa within the major zoological families represented, thereby sparing other researchers the time and expense of seeking to use CT equipment. Naturally, animals of divergent functional anatomy and osteology should be CTscanned. Lam et al. (2003) later argued that, in the absence of the opportunity to use technology to estimate bone mineral density in various elements, shape-corrected densitometer values can provide a reasonably reliable key to bone durability in bone without internal voids.

In their reviews of bone mineral density estimation methods, Lam and Pearson (2004, 2005) inserted an important methodological note: “Ironically, the increased technological sophistication of density studies have resulted in greater methodological variation than that observed among the original water displacement studies” (Lam and Pearson 2005: 102). They note that one of the main sources of the variability in VD estimates, besides those already outlined here, seems to be variation in different researchers’ scanning procedures, which they illustrate by divergent results in simple VD estimates of caprine elements in three studies (Lam and Pearson 2005: 102, Fig. 1). They note that many more researchers have attempted photon densitometer estimates than have done so with CTscanning and stress a need for explicit standardization of scanning procedures, which necessarily differ from the medical uses of single- or double-beam technology to scan bones in living tissues of patients. They thus call for new techniques and methods. As of the time of their publication, the authors were part of the only team to produce CTscan readings for a variety of skeletal elements and species, but they imply that a similar lack of uniformity in technique could emerge in using such technology.

21.1.3 Does a Negative Correlation Exist Between Nutritional Utility and Bone Durability?

Are the skeletal elements most likely to be selected for transport and processing because of their higher nutritional values also the most fragile in the skeleton and therefore, the most liable to be deleted by taphonomic processes? Lyman (1985, 1992) explored whether a negative relationship exists between utility indices and bone VD . If at least some high-utility bones have low volume density values, and some low-utility bones have high density values, he argued, this would present a problem in archaeological inference, because “inverse utility” curves could also result from in-place destruction of less durable elements. His reasoning was that elements or portions with considerable cancellous tissue were both reservoirs of nutrients (Chaps. 5 and 19) and more delicate than elements composed mainly of compact bone .

Lyman (1985, 1992) used Kendall’s tau (1985) or Spearman’s rho (1992) rank order correlation coefficients to assess the relationship between VD and various of Binford ’s utility indices, as well as indices developed by others for other animals. His results did not reveal uniform , statistically significant correlations, but they did reveal a consistent trend toward negative relations between VD and utility (Table 21.3). He later (1992) elaborated on this analysis by including nutritional data from more animals. This analysis also revealed a trend, though not always a statistically significant one, toward an inverse relationship between nutritional value and volume density (Table 21.4).
Table 21.3

Lyman’s Kendall’s tau rank-order correlation coefficients of volume (a.k.a bulk) density with caribou and sheep MGUI

Caribou

Kendall’s tau

VD:MGUI

−0·080 p = 0·540

Sheep

Kendall’s tau

VD:MGUI

−0·257 p = 0·047

Data is from Lyman (1985:228, Table 3)

Table 21.4

Lyman’s (1992: Table 2) Spearman’s rho rank-order correlation coefficients and P values between deer volume density (VD) and various published utility indices for artiodactyl species. These show consistently negative, but not always statistically significant, correlations of utility and MGUI

Utility index: VD

Utility w/ tongue

Utility w/out tongue

 

Rho

P

Rho

P

Sheep MGUIa

−0.295

0.11

−0.349

0.06

Caribou MGUIa

−0.116

0.54

−0.188

0.31

Complete-bone FUIb

−0.191

0.47

−0.212

0.42

Guanaco meat utilityc

−0.541

0.004

N/A

N/A

Guanaco modified utilityc

−0.309

0.09

N/A

N/A

Bison grease utilityd

N/A

N/A

−0.986

0.002

Bison modified total productsd

N/A

N/A

−0.308

0.10

Impalae

−0.65

0.018

N/A

N/A

Alcelaphine antelopee

−0.729

0.009

N/A

N/A

aBinford (1981)

bMetcalfe and Jones (1988)

cBorrero (1990)

dEmerson (1990)

eO’Connell et al. (1990)

Some may consider the existence of a trend rather than consistent, statistically significant correlations reason to dismiss Lyman ’s claims. However, in view of the problems outlined above in using with VD as an estimator of bone tissue density, it is worth asking whether BMD values derived from CTscans by Lam et al., rather than VD, would produce more compelling results. I explored this with caribou, a species for which MGUI and SFUI as well as BMD are known. Using the p ≤ 0.05 standard for significance, both results, p = 0.007 and p = 0.001, would be considered very statistically significant (Table 21.5). These results suggest that further evaluation of the inverse association between BMD and nutritional utility (MGUI /FUI ) for various species would be a useful step in zooarchaeological analysis.
Table 21.5

Spearman’s rho rank-order correlation coefficients and P values between caribou nutritional utility indices (see Table 20.​1) and caribou BMD (Table 21.1)

Utility index: BMD

Rho

P

Caribou MGUI

−0.4641

0.00745

Complete-bone FUI

−0.5765

0.00132

21.1.4 What Causes Destruction of More Fragile Elements or Portions of Elements?

Destructive processes affecting skeletal elements include consumption by carnivores , human culinary and consumption practices (marrow extraction, bone grease extraction, mashing and gnawing bone ends), human and animal traffic that crushes less dense bone, and post-depositional chemical and mechanical stresses , including the cumulative static loading of sedimentary layers. Whether and how one can tell which actor or other taphonomic process is involved in destruction of skeletal elements is a concern, and the lines of evidence outlined in Section 4 are relevant because actor/effector analysis can more closely specify the main process(es) that impacted an archaeofaunal sample. How to assess the dominant agent(s) of reduction in such assemblages is at present unclear, no “cookbook” approach exists for doing so. However, Chap. 17 provided examples of how various zooarchaeologists have approached this problem. Lyman (2008: 264–298) reviews the issues involved in tabulating such traces, which, like element frequencies , also become aggregate data , and he stressed (Lyman 1994: 335) that it is important to inspect existing specimens for percussion marks, carnivore action, and weathering , all of which are known to be related to processes that contribute to bone attrition , for hints at the processes and actors involved. The next section presents examples of how some zooarchaeologists have used bone mineral density and nutritional indices to explore the overlapping impacts of human selectivity and site formation.

21.1.5 How Can Knowledge of Bone Durability be Employed in Archaeofaunal Analysis?

This question can be rephrased as, is there a way to distinguish in situ destruction from selective transport ? Lyman (1985) suggested that, in addition to element frequencies , taphonomic and sedimentary evidence must be used to evaluate how heavily attritional processes may have affected an assemblage. For example, high frequencies of carnivore tooth marks or bone reduction patterns typical of carnivores on specimens should alert analysts to the possibility that such actors may have deleted less durable bones from the assemblage. In an application of his recommendations, Lyman (1985: 233) argued that Gatecliff Shelter ‘s (Thomas and Mayer 1983) inverse bulk utility pattern in the bighorn sheep assemblage could have been structured by forces other than human selectivity. Carnivore action is evident on specimens , and post-depositional rock falls affected the bone assemblage. He was careful to state that he has not “proved” that attrition rather than selective transport by humans is responsible for the curve. Rather, he urges circumspection in making such behavioral interpretations. Lyman noted that, in contrast, Speth ’s (1983) Garnsey archaeofauna shows very little evidence of carnivore action, fluvial transport, or weathering on the well-preserved bones. While skeletal parts of low utility were more abundant than those of high utility at the Garnsey Site , some high utility bones are present in very good states of preservation . Lyman argued that, in this case, the bone durability evidence supports Speth ’s interpretation of the assemblage as the product of human decisions based on relative utilities of elements.

Grayson (1988) analyzed the archaeofauna from Last Supper Cave , Nevada, and found a pattern of element representation for Ovis canadensis very similar to that of Gatecliff Shelter . Given Lyman ’s discussion of differential bone durabilities, he explored these in relation to VD and to MGUI , using Kendall's tau rank order correlation analysis. He proposed that inverse utility curves caused by human selection should show a significant negative correlation between MGUI and relative frequencies of elements, expressed as %MAU, which in the the era he was writing, was commonly used – see Chap. 18 (Grayson 1988: 70). By contrast, he contended that, in situations where only dense bones have survived attrition , there should be a significant positive correlation between VD and the element frequencies . With the Last Supper Cave assemblage, Grayson found that the relationship between VD :%MAU was positive and very significant, while that between %MAU :MGUI was negative but not significant. Gatecliff Shelter produced a similar result, with VD :%MAU , P = 0.0001, and a negative correlation of MGUI :%MAU p = 0.05. Without asserting a systematic relationship between MGUI and VD , Grayson inferred that these assemblages were more heavily affected by attrition than by human selectivity. On the basis of bone surface modifications, he concluded that carnivores are the most likely causal agents. Grayson also evaluated Anavik, Binford ’s Nunamiut kill-butchery site: the site showed no significant relationship between element frequencies and VD , but did display a highly significant negative correlation between frequency of skeletal element and MGUI , supporting Binford ’s description of activities there.

Lyman (1991) built on Grayson ’s predictive model in evaluating whether and how 67 ethnoarchaeological, archaeological, and paleontological faunas conformed to Grayson ’s 1988 predictions, using Spearman’s rho rank order correlation coefficients. Lyman constructed a nine-cell matrix (1991: 130), with significance values for %MAU :MGUI on one axis and those for %MAU :VD on the other. Lyman ’s results indicate that the Anavik kill-butchery fauna falls where it “should,” as a kill-butchery site from which high-utility elements had been removed, with a significant negative correlation between %MAU and MGUI and no positive correlation of %MAU :VD . Of special note is the fact that, despite archaeological evidence that some archaeofaunas derive from kill-butchery episodes, no archaeological sample displayed a similar pattern to Anavik’s, although some showed negative correlations of both %MAU :MGUI and %MAU :VD . Lyman interprets this as reflecting attrition by post-depositional taphonomic processes operating on the original element frequencies produced by human selectivity.

Taking a very different approach to the study of bone attrition , Cleghorn and Marean ( 2004) argued that the evidence for carnivore, especially spotted hyena (Crocuta crocuta), bone destruction in Pleistocene Eurasian and African archaeofaunas is so pervasive that methodological coping tactics were required. Since actualistic research on hyenas’ bone-destroying capabilities in captivity and in the wild (Marean et al. 1992; Blumenschine 1988; Marean and Spencer 1991; Capaldo 1998) are demonstrated, Marean and Cleghorn recommended that zooarchaeologists in any region with such large, bone-consuming carnivores use only the highest survival elements and portions of elements to estimate MNE . For long bones, these would be diaphyseal fragments, rather than epiphyseal ends; for skulls, these would be teeth and petrous bones (Bar-Oz and Dayan 2007). See also Marean et al. (2004) for a discussion of ignoring diaphyseal fragments in analyses.

Stiner (2002) objected to this and other arguments for diaphysis -based estimates of abundance on several grounds, citing agreements between shaft-based and epiphysis -based MNE estimates in the Palaeolithic Mediterranean archaeofaunas with which she had worked. Stiner also noted that published captive hyena feeding experiments used sheep elements and body segments, which the hyenas readily consumed. She stated that it was an open question whether the much larger ungulates recovered from Pleistocene archaeological sites would have been so completely reduced by Crocuta.

More recently, Janzen and Cleghorn (2010) presented data from experiments in the same hyena colony used by Marean et al., using domestic cattle vertebrae, scapulae, innominates, and femora, some of the latter whole, others broken and with marrow removed. They reported that the extent of bone destruction by hyenas in the experiment appeared to depend upon the social rank of the individual given the elements. Nevertheless, they found that hyenas were capable of demolishing even complete cattle femurs. As with the smaller animals, the hyenas consumed vertebrae leaving only a few scraps. Femoral portions were often consumed nearly completely, but differences were apparent in the treatment of shafts, depending upon whether the hyenas were presented with whole versus marrow -extracted bones. These data suggest that, if hyenas can have access to raw skeletal parts discarded by humans, larger axial elements often will be consumed, as will at least the epiphyses of long bones. Thus, the experiments established the species’ capabilities, as have Lupo’s (1995) observations on spotted hyena destruction of uncooked large ungulate elements hunted by Hadza foragers, and Blumenschine ’s and others’ field-based experiments cited above.

However, I believe Stiner is correct to note that not all of Crocuta’s former ranges displayed the levels of carnivore packing and interspecific competition observed in some parts of East Africa (Chap. 12). Lower rates of bone consumption are hinted at in African areas where hyena populations are less dense (e.g. Lam 1992; Egeland et al. 2008; Kruuk 1972). If at all possible, the prudent zooarchaeologist will seek contemporaneous paleontological information on carnivore species diversity before choosing a counting strategy, and checking both diaphyseal and epiphyseal estimates may be a good way to proceed. This is especially relevant in light of Morin et al.’s (2016) blind tests results, in which estimates based on long bone diaphyses were notably poor estimators of original skeletal element abundances (Chap. 18). Some have contested Stiner ’s (2002) anatomical region profiling method, but her careful cross checking of epiphyseal versus shaft MNE determinations is an intelligent way to explore the extent of BMD -based attrition , as are Grayson ’s (1988) statistical explorations.

These matters may seem only of concern to paleoanthropologists, but any zooarchaeologist who believes that their assemblages were affected by some form of serious mechanical attrition and considers using only high-survival elements should consider how this in turn may introduce the potential for sample-size effects, and hence reduced statistical power, in their estimates. Faith and Gordon (2007) used simulation studies to assess whether analysts following Cleghorn and Marean ’s recommendation to use only high-survival elements risk bringing their sample sizes below levels that produce reliable results. They evaluated sample-size effects on commonly applied measures of association employed to discern the influence of selectivity, such as correlations of %MAU with SFUI (Chap. 20). Their goal was to explore whether decreasing sample sizes affected the rates of Type I errors (in which significant correlations exist in the sample, but they do not in the parent population ) or Type II errors (in which no correlation exists in the sample, but a significant one exists in the parent population ).

Faith and Gordon used Pearson’s rho combined with the Shannon Evenness Index (Chap. 22) to explore sample-size effects may be obscuring patterns of selective transport . They drew from four populations of 1000 “high-survival” artiodactyl elements (Faith and Gordon 2007: 874, Table 1):
  1. 1.

    A parent population structured according to Binford ’s gourmet utility profile.

     
  2. 2.

    A parent population structured according to Binford ’s bulk utility profile.

     
  3. 3.

    A parent population structured according to Binford ’s “unbiased” sample, which represented skeletal elements at rates correlated with their nutritional value.

     
  4. 4.

    An “unconstrained” parent population , structured to include all elements in proportions commensurate with their frequencies in the skeleton, reflecting repeated cases of whole-body transport.

     

From each sample population, random draws of 250, 150, 100, and 50 elements were made, each 5000 times. The evenness (E) of the distribution of skeletal elements and Spearman’s rho correlation coefficients of SFUI to element frequencies were calculated for each draw.

For samples from the gourmet and unbiased populations, Type II errors increased as sample size decreased but remained relatively low. However, with bulk transport samples, where all but lowest utility elements are transported, Type II errors jumped from 1.9 to 48.7% as the sample MNE dropped from 250 to 50 (Faith and Gordon 2007: 876, Table 3). They conclude that bulk transport assemblages are especially sensitive to sample size effects . Recalling that the unconstrained parent population had no prior correlation between SFUI and element frequencies , Type I error rates are of interest: these occurred in 10–12% frequencies, regardless of sample size.

Applying the Shannon evenness index to each parent population and sample, the authors note that the bulk and unconstrained use patterns are quite similar, approaching or at 1.000, whereas the unbiased is “intermediate” in evenness (0.842), while the gourmet population, dominated by femora, has the greatest unevenness, at 0.369 (Faith and Gordon 2007: 876, Table 1). Reducing sample size differently affects evenness in samples drawn from the four populations. The gourmet strategy remains distinct from the others, regardless of sample size. At 250, the remaining three samples discriminate well from one another, but at 150 and 100 MNE , the evenness values of the bulk and unconstrained samples begin to overlap, while the unbiased sample remains distinct. At 50 elements, the bulk, constrained, and unbiased samples are indistinguishable. Faith and Gordon illustrate these points with three archaeofaunal analyses for which the data were available: Porc-Épic (Porcupine) Cave, Ethiopia, Die Kelders Cave , and Olduvai FLKN levels 1–2, showing possible sample size effects and possible transport strategies.

To sum up, when sample sizes drop below 150, correlation coefficients may not accurately reflect composition of the parent population . Samples from the relatively even, bulk, and unconstrained populations displayed greater Type II errors than did unbiased and gourmet samples. Bulk sample assemblages have the highest Type II error rates because a lack of correlation of SFUI with element frequencies is quite possible. Faith and Gordon argue that the Shannon evenness index can help analysts distinguish between transport strategies, although bulk and unconstrained transport strategies will produce similar evenness values. One should also recall that, except in mass kill situations, permutations of the bulk or unconstrained transport tactics were probably the most common accumulators of archaeofaunal deposits.

21.2 Why Use Only Element Frequencies?

At this point, one may well ask, what kind of an analyst would only use element frequencies to diagnose selective transport or effects of attritional processes? In the fractious debates about equifinality , this simple question often seems to get lost. Bone surface modification data, as citations above show, are key. If any assemblage lacks these data and is important enough to cite from the literature, it is important enough to reanalyze, if the collection has not been lost in the interim (see “Archaeological Sin,” Chap. 8).