ReviewThe potential for portable X-ray fluorescence determination of soil copper at ancient metallurgy sites, and considerations beyond measurements of total concentrations
Introduction
The production and use of metal objects is a key component of social complexity and emerges ∼8000 BCE with an initial focus on Cu (Killick and Fenn, 2012). Copper production also contributes Cu as a significant environmental pollutant, which, from limited studies to date, may potentially be found in extremely high concentrations at such sites around the world (Nagajyoti et al., 2010). This review focuses on examples of Cu contamination at metallurgy sites spanning the Neolithic (∼8000 BCE) to the mid first millennium BCE. More specifically, we focus on production sites (Cu smelting and metalworking) rather than mining sites.
Current earliest evidence for Cu working and the first instance of anthropogenic heavy metal pollution is at Neolithic sites (Grattan et al., 2016). The mining of native Cu and fabrication of Cu items rapidly expanded in the Chalcolithic (Copper Age) and by the Early Bronze Age production of Cu-based alloys included conditioning elements such as As and Sn (Harper, 1987, Killick and Fenn, 2012). From the Bronze Age, metallurgical practices involved sustained effort and increasingly complex and large scale operations (Killick and Fenn, 2012).
Ancient smelting sites are not typically situated within naturally mineralized zones (i.e. areas with naturally elevated background concentrations of heavy metals (Pryce et al., 2010)), although they may be within close proximity. This separation allows ready differentiation between natural and anthropogenic heavy metal contamination at these sites as such sites do not have an unknown degree of elevated ‘background’ contamination from mineralization. Examining Cu in particular at ancient smelting sites could provide insights into the longest term human-induced pollution.
Contemporary assessment of soil contamination from Cu typically focuses on soils that were contaminated over a relatively short time frame (years to decades, and in a very few studies, a few hundred years (e.g. Carr et al., 2008)). Assessment of contamination via total metal concentrations is an essential precursor (see Fig. 1) to more detailed investigations into element mobility, potential biological availability, and actual transfer into biota and foodchain at these sites to determine site specific risk of contamination (NEPC, 2013, Tighe et al., 2013). However, even this preliminary analysis is rarely undertaken (Frahm and Doonan, 2013).
Given the absence of these key baseline data on total soil Cu concentrations specifically at archaeometallurgy sites, we review what is known of total soil Cu at such sites, and explore the potential of portable X-ray Fluorescence spectrometry (pXRF) as a tool to address this shortcoming. We outline the major considerations in the application of this technology in this context with specific reference to practical considerations in quantifying Cu with this method. Assessing total soil Cu will provide new insights into the unintended consequences of metallurgically produced pollution on past societies, and can also enable preliminary assessment of the contemporary contamination risk such sites still pose. These baseline Cu data can additionally inform possible long term behaviour of a given level of contemporary contamination in similar environments.
Section snippets
Copper in the environment
Copper is a naturally occurring element which can be found in fauna, flora, rocks, volcanic dust and soil (Adrees et al., 2015, Ginocchio et al., 2006). Worldwide background values in soils range up to 110 mg kg−1 depending on parent material and soil texture, with an average of 14 mg kg−1 (Kabata-Pendias and Szteke, 2015). Copper forms strong bonds with sulfur, creating a range of Cu sulfide minerals such as covellite (CuS) and bornite (Cu5FeS4) (Kabata-Pendias and Szteke, 2015). When
pXRF technology and applications
Portable X-ray fluorescence spectrometers can analyse soil in situ or in a laboratory (US Environmental Protection Agency, 2007). These devices combine a miniaturized excitation source and multichannel analyser to enable simultaneous excitation (X-ray fluorescence) of target element energies and quantitative measurement. Characteristic X-ray emissions are elementally unique due to the binding energies specific to a particular element's electron configuration (McLaren et al., 2012a). For a brief
Beyond total soil concentrations- mobility and bioavailability of Cu
While total metal concentrations are the necessary first step in a tiered risk assessment of contamination and provide an initial indication of potential pollution via comparison with guideline values (NEPC, 2013), they can provide only limited approximations of ultimate pollution risk at any given site (Mariet et al., 2016, Tighe et al., 2013). Significantly elevated concentrations should trigger a move towards a more definitive assessment (Fig. 1). As with other metals, there is rarely a
Changes in the behaviour of Cu over time
Beyond the analysis of contamination risk, the analysis of Cu depth distributions in soils and sediments could augment archaeological and contemporary site interpretations. Analogous to many other archaeological and archaeometallurgical approaches, Cu concentration by soil depth could be either an indirect or direct (via dating) proxy for age. With a few notable exceptions at the local level (Hong et al., 1996b), and the more widely known global and regional palaeo-pollution assessments using
Conclusion
This review has focused on soil Cu contamination at ancient archaeometallurgy sites. Site remoteness, sample export difficulties, analysis time, and expense have hindered assessments of total soil concentrations of Cu at archaeological sites. Recent advances in pXRF technology and methods have the potential to address these issues. Caveats include careful considerations of precision and accuracy of pXRF use, as instrument set-up, energy settings, scan times and sample processing may all affect
Acknowledgements
This work was undertaken as part of a University of New England research seed grant. We thank two anonymous reviewers for their comments and suggestions.
References (69)
- et al.
A PXRF-based chemostratigraphy and provenience system for the Cooper's Ferry site, Idaho
J. Archaeol. Sci.
(2012) - et al.
Non-destructive PXRF analysis of museum-curated obsidian from the Near East
J. Archaeol. Sci.
(2012) - et al.
The technological versus methodological revolution of portable XRF in archaeology
J. Archaeol. Sci.
(2013) - et al.
Pottery production and distribution in prehistoric Bronze Age Cyprus. An application of pXRF analysis
J. Archaeol. Sci.
(2012) - et al.
Sedimentary metal-pollution signatures adjacent to the ancient centre of copper metallurgy at Khirbet Faynan in the desert of southern Jordan
J. Archaeol. Sci.
(2013) - et al.
The first polluted river? Repeated copper contamination of fluvial sediments associated with Late Neolithic human activity in southern Jordan
Sci. Total Environ.
(2016) - et al.
The local and global dimensions of metalliferous pollution derived from a reconstruction of an eight thousand year record of copper smelting and mining at a desrt-mountain frontier in southern Jordan
J. Archaeol. Sci.
(2007) - et al.
The geoarchaeology of “waste heaps” from the ancient mining and beneficiation of copper-rich ores in the Wadi Khalid in southern Jordan
J. Archaeol. Sci.
(2014) - et al.
Modern Bedouin exposures to copper contamination: an imperial legacy?
Ecotoxicol. Environ. Saf.
(2003) - et al.
A reconstruction of changes in copper production and copper emissions to the atmosphere during the past 7000 years
Sci. Total Environ.
(1996)