Characterisation of microbial attack on archaeological bone

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Abstract

As part of an EU funded project to investigate the factors influencing bone preservation in the archaeological record, more than 250 bones from 41 archaeological sites in five countries spanning four climatic regions were studied for diagenetic alteration. Sites were selected to cover a range of environmental conditions and archaeological contexts. Microscopic and physical (mercury intrusion porosimetry) analyses of these bones revealed that the majority (68%) had suffered microbial attack. Furthermore, significant differences were found between animal and human bone in both the state of preservation and the type of microbial attack present. These differences in preservation might result from differences in early taphonomy of the bones.

Introduction

Bone is used extensively as a source of information in archaeological research as it is usually the only animal or human tissue preserved, though often it is altered or destroyed as well. With the development of biomolecular analysis, the significance of understanding bone preservation has increased. One of the earliest types of alteration is microbial attack. Yoshino et al. [42]observed evidence of microbial alteration in bone 5 years post-mortem, indeed Haversian canals were (still) filled with bacteria. Bell et al. [5]found evidence of microbial attack in bone in a forensic study, as soon as 3 months post mortem, though this sample was recovered from a predator scat.

Biological alteration in bone is in most cases caused by fungi [31], bacteria [2], [14], [23], or cyanobacteria in marine environments [4]. Wedl first described microbial attack on mineralised tissue in 1864, finding tunnels of approximately 8 μm in diameter in sections of teeth exposed to untreated well water and in fossil reptile teeth. This type of tunnelling is defined as Wedl or centrifugal tunnelling by Hackett [14]. These tunnels range in diameter from 5 to 10 μm and under electron microscopy [31]appear empty with well-defined calcified walls, implying that collagen and mineral are both resorbed by the fungi.

Three types of microscopical focal destruction (mfd)—described by Hackett as ‘linear longitudinal’, ‘budded’ and ‘lamellate’—are generally assumed to be caused by bacteria. These mfd can be distinguished histologically by morphology; size, shape, the presence of a hypermineralised rim and the presence of a lamellate content. Under light microscopy these mfd show a granulous or fibrillar content, but higher magnification shows that their interior actually consists of small pores [2], [23], [40]. Mercury intrusion porosimetry (HgIP) shows an increased volume in pores with diameters in the 0.1–10 μm region, with the largest increase observed at approximately 0.6 and 1.2 μm [35], [40], consistent with the average diameter for bacteria (0.5 μm [18]). Indeed, Baud and Lacotte [2]argue that the small pores that are visible at electron microscope level are the mineralised remains of bacteria, in which case they would not form the interconnected porosity observed by Turner-Walker et al. [40].

We report here some results from a European study, which attempted to identify the key contributory factors to bone deterioration. Biological alteration of archaeological bone is a widespread phenomenon apparently not limited to a single burial environment [21]. Its effect on bone preservation is important as it can accelerate degradation by increasing the bone porosity [35]and simultaneously reduces chances of success for biomolecular research through loss or contamination of target molecules [9]. Two methodological approaches, mercury intrusion porosimetry (HgIP) and histology, are combined for the first time in this project. While histology has been widely used previously to characterise microbial attack (e.g. [3], [11], [14]), HgIP makes it possible to analyse a larger sample of bone and provides quantitative results [40].

Section snippets

Materials and methods

Samples of animal and human bone and related soil were taken from excavations in Sweden, theNetherlands, the United Kingdom, Italy and Turkey, spanning four climatic regimes (Mediterranean, Continental, Maritime (coastal) and Subarctic) (Appendix A). The 41 sites were chosen on the basis of well-defined geological and archaeological context and documented environmental parameters such as ground water table, annual rainfall and land use history. Sites ranged from the Neolithic to early modern

Characterisation of microbial attack

Two hundred and sixty-one bone samples from 41 different archaeological sites were analysed using histology and 233 samples of these using mercury intrusion porosimetry as well. Of the samples analysed histologically (n=261), 177 samples showed microbial attack (68%). Only 9% of the total sample could be considered well preserved. In 12% of the bones the characteristic ‘Apigliano style degradation’ [38]could be observed. Apigliano style degradation is characterised by highly crystalline and

Discussion

In this study we used the combination of histology and mercury intrusion porosimetry to characterise microbial attack. The porosity traces of all types of bacterial tunnelling showed a double peak, with increases in the pore volume at about 0.6 μm and 1.2 μm; albeit the former was smaller in the lamellate tunnelling (0.3 μm). Most bones with lamellate tunnels were found on very similar sites (large, densely occupied, medieval cemeteries). The smaller pores may therefore reflect differences in

Conclusion

Microbial attack is an important contributor to bone deterioration. HgIP and histology can be used to detect its effects. While HgIP analyses a larger sample volume and gives quantitative results, histology is needed to distinguish between bacterial and fungal attack. Bone from complete burials (animal and human) is more likely to be affected by bacterial attack indicating that bacterial degradation is linked to putrefaction and the very early stages of degradation. The majority of bone, which

Acknowledgements

This project has been carried out with financial support of the European Union, Directorate General No. XII, in the framework of the Environment and Climate programme (1994–1998), project no. ENV4-CT98-0712. Prof. John N. S. Matthews (University of Newcastle) is gratefully acknowledged for his help with the statistical analysis. Two anonymous reviewers are thanked for their valuable comments.

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