The use of fire played an important role in the social and technological development of the genus Homo. Most archaeologists agree that this was a multi-stage process, beginning with the exploitation of natural fires and ending with the ability to create fire from scratch. Some have argued that in the Middle Palaeolithic (MP) hominin fire use was limited by the availability of fire in the landscape. Here, we present a record of the abundance of polycyclic aromatic hydrocarbons (PAHs), organic compounds that are produced during the combustion of organic material, from Lusakert Cave, a MP site in Armenia. We find no correlation between the abundance of light PAHs (3–4 rings), which are a major component of wildfire PAH emissions and are shown to disperse widely during fire events, and heavy PAHs (5–6 rings), which are a major component of particulate emissions of burned wood. Instead, we find heavy PAHs correlate with MP artifact density at the site. Given that hPAH abundance correlates with occupation intensity rather than lPAH abundance, we argue that MP hominins were able to control fire and utilize it regardless of the variability of fires in the environment. Together with other studies on MP fire use, these results suggest that the ability of hominins to manipulate fire independent of exploitation of wildfires was spatially variable in the MP and may have developed multiple times in the genus Homo.
The use of fire played a key role in the evolution of the genus Homo1, allowing for warmth, cooking, birch tar production, protection from predators, a venue for social interactions and access to high latitudes and dark caves2. Evidence of hominin fire use is present in the archaeological record beginning around 1.5 million years ago3,4,5, and while it has long been assumed that a variety of hominin species could use fire5,6,7, the degree to which hominins were able to intentionally create and control fire (pyrotechnology) is debated8,9,10,11,12,13,14,15,16,17. Recently, some have argued that this ability was exclusive to modern humans9,12,16, with other hominins, such as Neanderthals, limited to exploiting wildfires. Neanderthals went extinct during the late Pleistocene. The reasons for that extinction remain unclear, and recent genetic data indicate that Neanderthal DNA persists among certain modern populations of Homo sapiens18. Neanderthal extinction has been linked specifically or in combination to fire use, foraging behaviors, a lack of clothing, demography, climate change, and interactions with expanding populations of Upper Palaeolithic Homo sapiens19,20. Evidence for the use of fire among MP hominins includes burning found in archaeological sites, and the construction of hearths. Manganese dioxide blocks, which are useful for fire-starting, have also been excavated at MP sites and are interpreted by some as evidence of Neanderthal fire production21. However, research at MP sites in France claims that fire frequency, measured by thermally altered flint and burnt bone, is positively correlated with warmer periods, when wildfire frequency is assumed to be highest, rather than with colder, glacial periods when fire use would have provided greater benefit; this correlation is derived by associating chronometrically dated stratigraphic layers at these sites with particular phases of Pleistocene global temperature records. These data are collectively interpreted as evidence that Neanderthals had not mastered pyrotechnology, and instead harvested natural fires caused by lightning strikes12,16, though this interpretation is not accepted by all15.
In order to test the hypothesis that MP hominin fire use was correlated with natural fire frequency, we developed a record of polycyclic aromatic hydrocarbons (PAHs) for the MP site of Lusakert Cave 1 (LKT1) in the Armenian Highlands from eighteen sedimentary units associated with MP lithic technology22,23,24. Organic molecular markers of fire, including PAHs, can provide a quantitative record of fire over geological time scales25,26, though lighter PAHs may be more susceptible to the effects of degradation due to their higher solubility27. During biomass combustion PAHs with variable structure are formed typically containing two (e.g. naphthalene) to six (e.g. benzo[g, h, i]perylene) rings (Supplementary Fig. S1). A number of studies have documented the PAH emission from wood burning in hearths and fireplaces28,29,30,31,32,33. While varied PAHs are produced during wood combustion, low molecular weight PAHs (lPAHs) with four or fewer rings concentrate in the gaseous phase, whereas high molecular weight PAHs (hPAHs), with five or more rings tend to concentrate in the particulate phase34,35,36. Hearths in archaeological contexts can reach maximum temperatures of 1000 °C with mean temperatures of 600 °C, which provides sufficient energy for the production of hPAHs37,38.
Unlike wood combustion in hearths, studies document the low production of hPAHs in wild fires of varying intensities, which produce mostly 3- and 4-ring PAHs. For example, soils measured in a recently burned area in southern France did not measure hPAH abundances higher than control samples39. Following forest fires in South Korea, lPAH concentrations were found to be 3 to 28 times higher than hPAH concentrations40. Soil O-horizons in Russia analyzed two, ten and 16 years after a wildfire found that hPAH concentrations were not higher than background soils, despite 9-fold increases in total PAH concentrations41. hPAHs comprised 35% of the total PAH load in unburnt samples from fire prone regions in Spain, but less than 10% in burnt soils after wildfires due to the addition of lPAHs42. Finally, in savannah fires in Australia the frequency of emitted lPAHs was 13 to 30 times greater than hPAHs43. These data attest to the widespread production and dispersal of lPAHs associated with wildfire events.
In sedimentary records from fire-prone regions, hPAHs are typically lower in abundance than lPAHs44,45. Different explanations have been given for the lack of hPAHs relative to lPAHs, including changes in temperature or burn intensity44, as higher molecular weight PAHs require higher activation energies for synthesis. Another potential explanation is the proximity to the source of the fire45, as hPAHs are less likely to travel from the source of the fire. Therefore, in the context of a spatially confined archaeological site such as LKT1, we expect that the primary mode of deposition of lPAHs will be through long-range dispersals of wildfire, whereas the primary mode of deposition of hPAHs will be local fire use within the cave by hominins. Given the low abundance of hPAHs produced during wildfires relative to lPAHs, and their concentration in the particulate emissions from wood burned in hearths, it is the most parsimonious explanation that accumulation of hPAHs in the sediments of archaeological sites like Lusakert Cave will be due to increased particulate deposition of residues from wood combustion. These particulate emissions of hearths will concentrate locally, on the scale of 10 s of meters.
In addition to PAH data for local or regional fire, we also analyzed the hydrogen (δDwax) and carbon (δ13Cwax) isotope composition of long-chain n-alkanes, the molecular remains of epicuticular waxes of terrestrial plants, to constrain regional climate and hydrology through the period of hominin occupation (Fig. 1A,B). Like hPAHs and lPAHs, n-alkanes are preserved over geological time scales. Long-chain n-alkanes at LKT1 have high odd-over-even predominance (OEP), demonstrating that they did not undergo significant microbial46 or thermal47 alteration (Supplementary Table S2). The δ13C values in plant material is primarily a reflection of the photosynthetic pathway of the plant (C3, C4 or CAM). In C3 plants, δ13C values are influenced by physiological changes as plants balance water loss and CO2 uptake through the regulation of stomata, altering the partial pressures of intracellular (Ci) relative to extracellular (Ca) CO248,49, causing a positive shift in δ13C values in C3 plants experiencing water stress50. Fractionation during lipid biosynthesis causes n-alkane δ13C values to be lower relative to bulk plant tissues51,52. Therefore, sedimentary δ13Cwax values of n-alkanes predominantly reflect plant photosynthetic type and factors that affect isotopic discrimination during carbon fixation53. δDwax record the isotope values of ambient water during the period of growth54, reflecting mostly precipitation isotope values in terrestrial systems. δD values of precipitation are influenced by temperature, amount of precipitation, and cloud transport history55,56. Most of the variability in modern precipitation δD values in the Armenian Highlands is explained by changes in temperature, and there is no significant trend associated with amount of precipitation57. This is also documented in Global Network of Isotopes in Precipitation stations in Georgia and Turkey (Supplementary Fig. S3). Hydrogen undergoes further fractionation during lipid biosynthesis, which is influenced by the timing of wax formation, plant physiology and functional type58,59,60.
LKT1 was excavated by an Armenian-American-British team between 2008 and 2011 and is one of the few sites in the region that preserves stratified assemblages of lithic and faunal material (Supplementary Discussion S4, Supplementary Fig. S5). In addition, there is extensive evidence for fire in the form of charcoal and visible combustion structures, as well as thermally altered bone micro-fragments in micromorphological samples (Supplementary Figs S6, S7, S8). The lithic assemblage is made entirely of obsidian from a variety of local (<25 km) and exotic (>25 km) sources, it is based on the Levallois method, and it can be classified as Middle Palaeolithic, a toolkit traditionally associated with Neanderthals in the Caucasus and neighboring regions22,23. Preliminary luminescence and AMS radiocarbon dates, as well as tephrochronological correlations constrain the stratigraphy of the site to 60–40 ka.
Results and Discussion
At LKT1, δ13Cwax values increased during the period of deposition (Fig. 1A), which is best explained by an increase in the proportion of C4 vegetation or C3 vegetation undergoing water stress. δDwax shows a clear shift to more positive values in the middle of the depositional sequence (Fig. 1B), which modern data show is best explained by changes in regional or global temperature through the period of deposition. By coupling these palaeoenvironmental proxy data with molecular records of local and regional fire intensity, we can test whether fire use among MP hominins was predicated on climate (natural availability) or behavior (pyrotechnology). If climate, as recorded by δDwax and δ13Cwax, dictated fire use by hominins, we would expect a correlation between natural fire availability (lPAHs) and on-site fire frequency (hPAHs). If hominin pyrotechnology drove fire use, we would not expect to see a strict correlation between climate and fire frequency.
The combined record of local fire (hPAHs), regional fire (lPAHs), vegetation (δ13Cwax) and temperature (δDwax) change documented at LKT1 demonstrates that MP hominins used fire in the cave during periods of low wildfire abundance, as recorded by lPAHs (Fig. 1). We find that there is no significant correlation (Spearman’s ρ = 0.141, p = 0.575) between lPAHs and hPAHs within samples, which decouples local fire frequency at the site from regional fire frequency (Fig. 1C, Supplementary Table S9). Layers 5 and 6, where the highest concentrations of hPAHs were measured, correspond with low frequencies of lPAHs. High concentrations of hPAHs were not always measured in archaeological layers with visible hearth features or other indications of fire use, for example in Layer 4 which contains abundant charcoal fragments and burnt bone fragments. In addition, high concentrations of hPAHs in Layers 5 and 6 correspond to the highest artifact densities, which can be correlated with increased occupation intensity (Fig. 2). The inverse is documented in strata above and below Layers 5 and 6 (i.e. Layers 3, and 10.1–10.3), where artifact density and hPAHs are lowest. This relationship between PAHs and artifact concentration is true no matter how we normalize the PAH concentration (to sediment weight or n-alkane concentration) and is not dependent on sediment type (Supplementary Fig. S10). These data show that since artifact density is correlated with hPAH concentrations (Fig. 3, Pearson’s r = 0.826, p < 0.05) rather than wild fire frequency, MP hominins at the site were able to habitually control fire, and that these activities were independent of climate (i.e. natural fires).
At LKT1, the most abundant hPAHs are B(a)P (8 layers), B(k)F (8 layers) and B(b)F (2 layers). In a series of experiments on wood combustion in fireplaces and wood stoves, B(a)P is the most abundant hPAH produced of those measured in this study in 20 of the 29 different species of wood with B(k)F the most abundant in 8 species and B(b)F the most abundant in 129,61,62,63. Overall, the abundance of hPAHs in these modern wood combustion studies is (in order most abundant to least): B(a)P > B(k)F > B(b)F > I(1,2,3-cd)P + D(a, h)A > B(g, h, i)P. This order of abundance is the same as the averaged abundance for the layers at Lusakert, B(a)P > B(k)F > B(b)F > I(1,2,3-cd)P + D(a, h)A > B(g, h, i)P (Supplementary Fig. S11). The relationship between the abundances of different hPAHs at LKT1 and those emitted from burnt wood is significant (Pearson’s r = 0.861, p < 0.05). B(a)P does seem to be more abundant relative to other hPAHs than in the modern wood burning study, however, other studies demonstrate similar high abundances of B(a)P relative to other hPAHs in burning of pine wood with green needles and savanna grasses (Supplementary Fig. S11)64. lPAH abundance at LKT1 is similar to those of gaseous emissions of open burns of straw (Pearson’s r = 0.742, p < 0.10), which may be a reflection of the open environment suggested by the high δ13Cwax values65.
Other potential causes for the inversion of the relative concentration of hPAH and lPAH abundance in Units 5 and 6 at LKT1 include the loss of lPAHs due to postdepositional effects. The solubility of hydrocarbons like PAHs and n-alkanes are correlated with their molecular weight, and as such lower molecular weight PAHs and n-alkanes are more susceptible to degradation. Denis et al.27 argue that sedimentary units with lPAH concentrations greater than hPAH concentrations are indicative of favorable conditions for organic preservation27. This is observed in Units 3, 4, 7 and 10 at Lusakert, but not in Units 5 and 6. However, based on the consistently high OEP values, n-alkanes at the site do not show any increase in degradation in Units 5 and 6 (Supplemental Information 2). We do not expect changes in preservation potential based on lithologies of the sedimentary units given the relatively consistent depositional environment and grain size through the sequence (Supplemental Information 4). Given the preservation of other hydrocarbons, we argue that the changes in hPAH concentrations at LKT1 is reflective of changes in PAH production, rather than variable preservation.
This coupled record of fire and climate also shows the drivers of fire frequency in the past in the Armenian Highlands. There is a significant positive correlation between lPAHs and δ13Cwax values (Spearman’s ρ = 0.513, p = 0.029) and no significant relationship with δDwax values (Spearman’s ρ = 0.210, p = 0.403), suggest wild fire frequency (lPAHs) is not determined by temperature, but rather by changes in vegetation. More positive δ13Cwax values, representing more open habitats, are associated with higher frequencies of wild fire, whereas more negative δ13Cwax values, associated with more closed habitats, are associated with lower frequencies of wildfire. Other studies have observed this correlation between δ13Cwax values and lPAH concentration66. This is consistent with research on modern wildfires, the frequency of which is not only determined by the frequency of ignition agents (e.g. lightning strikes), but also by a number of variables including precipitation and net primary productivity67. Though global wildfire activity in the Holocene may correlate with temperature68, records of Holocene fire frequency in the Armenian Highlands co-varied with vegetation and aridity changes69.
At LKT1, the most robust evidence for fire (hPAHs) correlates with periods during which wildfires (lPAHs) were at their lowest frequency and occupation intensity was at its highest. Therefore, we can reject the hypothesis that fire use among MP hominins was predicated on its natural occurrence in the regional environment. We interpret the evidence as indicating the habitual use of fire by MP hominins during periods of low wildfire frequency. While these data do not preclude the interpretation that MP hominins were harvesting and maintaining wildfires, given that wildfire was still present on the landscape during all periods of occupation at the site, we conclude that the combined evidence demonstrate that MP hominins exhibited significant control over fire, and likely pyrotechnology.
These results suggest that pyrotechnology existed among MP hominins. However, its true antiquity has yet to be determined, and evidence for fire creation exists at 50 ka13 and evidence for its control dates to earlier than 300 ka6,14. If the contradictory evidence from MP sites in France is correct, these data suggest that MP fire use was regionally differentiated. This would suggest that the ability of hominins to control and perhaps create fire was either (1) a primitive behavioral trait that was lost in certain MP populations, or (2) a behavioral trait derived independently among MP populations. In either case, it follows that pyrotechnology was not limited to Upper Palaeolithic Homo sapiens and therefore unlikely to have played any role in the demise of MP hominins such as the Neanderthals. By applying the methods outlined here to Palaeolithic sites elsewhere in Eurasia and Stone Age sites in Africa, we will be able to determine what, if any, spatio-temporal patterns exist in pyrotechnology, and how such patterns might be equated with particular hominin species, environments, or climates.
Sample collection and extraction
We collected 18 sediment samples (~150 g) in the summer of 2014 from each sedimentary unit in Profile 4 at LKT1. We stored these samples at −20 °C, and they were lyophilized prior to lipid extraction. Lipids were extracted from the sediment via Soxhlet extraction in 300 mL of 2:1 dichloromethane:methanol for 48 hours. Following lipid extraction, we saponified the total lipid extract by heating the sample for 2 hours at 85 °C with 5 mL of 1 M KOH in methanol. We stopped the reaction by cooling to room temperature and adding 5 mL of 5% sodium chloride in water. We then extracted neutral compounds with a liquid/liquid extraction. n-alkanes and PAHs were separated from total liquid extract by passing samples through a column of activated silica gel (1.25 g) in baked Pasteur pipettes with 2 mL hexane (non-polar fraction), 4 mL dichloromethane (slightly polar fraction) and 4 mL methanol (polar fraction). n-alkanes were quantified through the analysis of the hexane fraction and PAHs were quantified through the analysis of the dichloromethane fraction. We did not identify PAHs in the hexane soluble fraction.
n-alkanes and PAHs were measured on a Trace Gas Chromatograph (GC) Ultra (Thermo-Scientific) fitted with a split–splitless (SSL) injector and flame ionization detector (FID). We quantified n-alkanes using a BP-5 column (30 m × 0.25 mm i.d., 0.25 μm film thickness) with He as the carrier (1.5 ml/min). Oven temperature was set at 50 °C for 1 min, ramped to 180 °C at 12 °C/min, then ramped to 320 °C at 6 °C/min and held for 4 min. We measured PAHs using a DB-5 column (60 m × 0.25 mm i.d., 0.25 μm film thickness) with He as the carrier (1.5 ml/min). Oven temperature was set at 70 °C and held for 4 minutes, ramped to 180 °C at a rate of 15 °C/min, ramped to 290 °C at 4 °C/min, then ramped to 310 °C at 5 °C/min and held for 19 minutes. Samples were analyzed in concert with a 16 component PAH standard (Restek SV Calibration Mix #5/610 PAH mix, Bellefonte PA, USA) at known concentrations ranging from 0.25 to 400 ng for calibration and quantification. Calibration mixes were also analyzed via Gas Chromatography-Mass Spectrometry (GC-MS) on an Agilent 6890 at the University of Connecticut with a relative standard error of 4%.
Stable isotope analysis
The δD and δ13C values of individual n-alkanes were measured with a GC-Isolink coupled to a MAT 253 Isotope Ratio Mass Spectrometer (IRMS) (Thermo Scientific) with a BP-5 column (30 m × 0.25 mm i.d., 0.25 μm film thickness) at the University of Connecticut. Oven temperature and ramp was identical to the method used for n-alkane measurement. Isotopic standards (Mix A from A. Schimmelman) were analyzed every four samples across a range of concentrations to correct for size and scale effects. Standard deviations were 0.5‰ for δ13C (n = 7) and 4‰ for δD (n = 9). Stable isotopic composition is expressed in standard delta notation relative to VPDB and VSMOW.
All data discussed in the paper is in this article and its Supplemental Information.
Wrangham, R. & Carmody, R. Human adaptation to the control of fire. Evol. Anthropol. 19, 187–199 (2010).
Mallol, C. & Henry, A. Ethnoarchaeology of Paleolithic Fire: Methodological Considerations. Curr. Anthropol. 58, S000–S000 (2017).
Berna, F. et al. Microstratigraphic evidence of in situ fire in the Acheulean strata of Wonderwerk Cave, Northern Cape province, South Africa. Proc. Natl. Acad. Sci. 109, E1215–E1220 (2012).
Hlubik, S., Berna, F., Feibel, C., Braun, D. & Harris, J. W. K. Researching the Nature of Fire at 1.5 Mya on the Site of FxJj20 AB, Koobi Fora, Kenya, Using High-Resolution Spatial Analysis and FTIR Spectrometry. Curr. Anthropol. 58, S243–S257 (2017).
Gowlett, J. A. J. The discovery of fire by humans: a long and convoluted process. Philos. Trans. R. Soc. B 371, 20150164 (2016).
Roebroeks, W. & Villa, P. On the earliest evidence for habitual use of fire in. Europe. Proc. Natl. Acad. Sci. 108, 5209–5214 (2011).
Shimelmitz, R. et al. ‘Fire at will’: The emergence of habitual fi re use 350, 000 years ago. J. Hum. Evol. 77, 196–203 (2014).
Chazan, M. Toward a Long Prehistory of Fire. Curr. Anthropol. 58, S000–S000 (2017).
Sandgathe, D. M. Identifying and Describing Pattern and Process in the Evolution of Hominin Use of Fire. Curr. Anthropol. 58, S000–S000 (2017).
Henry, A. G. Neanderthal Cooking and the Costs of Fire. Curr. Anthropol. 58, S000–S000 (2017).
Dibble, H. L., Sandgathe, D., Goldberg, P., McPherron, S. & Aldeias, V. Were Western European Neandertals Able to Make Fire? J. Paleolit. Archaeol. https://doi.org/10.1007/s41982-017-0002-6 (2018).
Aldeias, V. et al. Evidence for Neandertal use of fire at Roc de Marsal (France). J. Archaeol. Sci. 39, 2414–2423 (2012).
Sorensen, A. C., Claud, E. & Soressi, M. Neandertal fire-making technology inferred from microwear analysis. Sci. Rep. 8, 1–16 (2018).
Shimelmitz, R. et al. ‘Fire at will’: The emergence of habitual fire use 350,000 years ago. J. Hum. Evol. 77, 196–203 (2014).
Sorensen, A. C. On the relationship between climate and Neandertal fire use during the Last Glacial in south-west France. Quat. Int. 436, 114–128 (2017).
Sandgathe, D. M., Dibble, H. L., Goldberg, P., Mcpherron, S. P. & Hodgkins, J. On the Role of Fire in Neandertal Adaptations in Western Europe: Evidence from Pech de l’Azé IV and Roc de Marsal, France. PaleoAnthropology 216–242 (2011).
Sorensen, A. C. & Scherjon, F. fiReproxies: A computational model providing insight into heat-affected archaeological lithic assemblages. PLoS One 13, 1–25 (2018).
Green, R. E. et al. A Draft Sequence of the Neandertal Genome. Science (80-.). 328, 710–722 (2010).
Roebroeks, W. & Soressi, M. Neandertals revised. Proc. Natl. Acad. Sci. 113, 6372–6379 (2016).
Goldfield, A. E., Booton, R. & Marston, J. M. Modeling the role of fire and cooking in the competitive exclusion of Neanderthals. J. Hum. Evol. 2018 (2018).
Heyes, P. J., Anastasakis, K., Jong, W. D. & Hoesel, A. V. Selection and Use of Manganese Dioxide by Neanderthals. Sci. Rep. 1–9 (2016).
Gasparyan, B. et al. The Middle Paleolithic Occupation of Armenia: Summarizing Old and New Data. In Stone Age of Armenia: A Guide-book to the Stone Age Archaeology in the Republic of Armenia (eds Gasparyan, B. & Arimura, M.) 65–105 (Monograph of the JSPS-Bilateral Joint Research Project, Kanazawa University Press, 2014).
Adler, D. S. et al. The Hrazdan Gorge Palaeolithic Project, 2008–2009. In Archaeology of Armenia in Regional Context, Proceedings of the International Conference dedicated to the 50th Anniversary of the Institute of Archaeology and Ethnography (eds Avetisyan, P. & Bobokhyan, A.) 22–38, https://doi.org/10.1017/CBO9781107415324.004 (Gitutyun, 2012).
Frahm, E. et al. Lithic raw material units based on magnetic properties: A blind test with Armenian obsidian and application to the Middle Palaeolithic site of Lusakert Cave 1. J. Archaeol. Sci. 74, 102–123 (2016).
Nabbefeld, B., Grice, K., Summons, R. E., Hays, L. E. & Cao, C. Significance of polycyclic aromatic hydrocarbons (PAHs) in Permian/Triassic boundary sections. Appl. Geochemistry 25, 1374–1382 (2010).
Marynowski, L., Scott, A. C., Zatoń, M., Parent, H. & Garrido, A. C. First multi-proxy record of Jurassic wildfires from Gondwana: Evidence from the Middle Jurassic of the Neuquén Basin, Argentina. Palaeogeogr. Palaeoclimatol. Palaeoecol. 299, 129–136 (2011).
Denis, E. H., Pedentchouk, N., Schouten, S., Pagani, M. & Freeman, K. H. Fire and ecosystem change in the Arctic across the Paleocene–Eocene Thermal Maximum. Earth Planet. Sci. Lett. 467, 149–156 (2017).
Gonçalves, C. et al. Organic compounds in PM2.5 emitted from fireplace and woodstove combustion of typical Portuguese wood species. Atmos. Environ. 45, 4533–4545 (2011).
Fine, P. M., Cass, G. R. & Simoneit, B. R. T. Chemical Characterization of Fine Particle Emissions from Fireplace Combustion of Woods Grown in the Northeastern United States. Environ. Eng. Sci. 35, 2655–2675 (2001).
Achten, C., Beer, F. T., Stader, C. & Brinkhaus, S. G. Wood-Specific Polycyclic Aromatic Hydrocarbon (PAH) Patterns in Soot Using Gas Chromatography-Atmospheric Pressure Laser Ionization-Mass Spectrometry (GC-APLI-MS). Environ. Forensics 16, 42–50 (2015).
Orasche, J. et al. Comparison of Emissions from Wood Combustion. Part 2: Impact of Combustion Conditions on Emission Factors and Characteristics of Particle-Bound Organic Species and Polycyclic Aromatic Hydrocarbon (PAH)-Related Toxicological Potential. Energy and Fuels 27, 1482–1491 (2013).
Djinovic-Stojanovic, J., Popovic, A., Spiric, A. & Jira, W. Emission of polycyclic aromatic hydrocarbons from beech wood combustion. Energy Sources, Part A Recover. Util. Environ. Eff. 35, 328–336 (2013).
Gullett, B. K., Touati, A. & Hays, M. D. PCDD/F, PCB, HxCBz, PAH, and PM emission factors for fireplace and woodstove combustion in the San Francisco Bay region. [Erratum to document cited in CA138:291832]. Environ. Sci. Technol. 38, 3792 (2004).
Schauer, J. J., Kleeman, M. J., Cass, G. R. & Simoneit, B. R. T. Measurement of Emissions from Air Pollution Sources. 3. C 1 −C 29 Organic Compounds from Fireplace Combustion of Wood. Environ. Sci. Technol. 35, 1716–1728 (2001).
Mcdonald, J. D. et al. Fine particle and gaseous emission rates from residential wood combustion. Environ. Sci. Technol. 34, 2080–2091 (2000).
Hytönen, K. et al. Gas-particle distribution of PAHs in wood combustion emission determined with annular denuders, filter, and polyurethane foam adsorbent. Aerosol Sci. Technol. 43, 442–454 (2009).
March, R. J., Lucquin, A., Joly, D., Ferreri, J. C. & Muhieddine, M. Processes of Formation and Alteration of Archaeological Fire Structures: Complexity Viewed in the Light of Experimental Approaches. J. Archaeol. Method Theory 21, 1–45 (2014).
Aldeias, V. Experimental Approaches to Archaeological Fire Features and Their Behavioral Relevance. Curr. Anthropol. 58, S000–S000 (2017).
Vergnoux, A., Malleret, L., Asia, L., Doumenq, P. & Theraulaz, F. Impact of forest fires on PAH level and distribution in soils. Environ. Res. 111, 193–198 (2011).
Kim, E. J., Choi, S. D. & Chang, Y. S. Levels and patterns of polycyclic aromatic hydrocarbons (PAHs) in soils after forest fires in South Korea. Environ. Sci. Pollut. Res. 18, 1508–1517 (2011).
Dymov, A. A. & Gabov, D. N. Pyrogenic alterations of Podzols at the North-east European part of Russia: Morphology, carbon pools, PAH content. Geoderma 241–242, 230–237 (2015).
Campo, J., Lorenzo, M., Cammeraat, E. L. H., Picó, Y. & Andreu, V. Emerging contaminants related to the occurrence of forest fires in the Spanish Mediterranean. Sci. Total Environ. 603–604, 330–339 (2017).
Wang, X. et al. Emissions of Selected Semivolatile Organic Chemicals from Forest and Savannah Fires. Environ. Sci. Technol. 51, 1293–1302 (2017).
Denis, E. H. et al. Polycyclic aromatic hydrocarbons (PAHs) in lake sediments record historic fire events: Validation using HPLC-fluorescence detection. Org. Geochem. 45, 7–17 (2012).
Argiriadis, E. et al. Lake sediment fecal and biomass burning biomarkers provide direct evidence for prehistoric human-lit fires in New Zealand. Sci. Rep. 8, 2–10 (2018).
Brittingham, A., Hren, M. & Hartman, G. Microbial alteration of the hydrogen and carbon isotopic composition of n-alkanes in sediments. Org. Geochem. 107, 1–8 (2017).
Wang, C., Eley, Y., Oakes, A. & Hren, M. Hydrogen isotope and molecular alteration of n-alkanes during heating in open and closed systems. Org. Geochem. 112, 47–58 (2017).
Farquhar, G. D., Ehleringer, J. R. & Hubick, K. T. Carbon Isotope Discrimination and Photosynthesis. Annu. Rev. Plant Physiol. Plant Mol. Biol. 40, 503–537 (1989).
Cernusak, L. A. et al. Environmental and physiological determinants of carbon isotope discrimination in terrestrial plants. New Phytol. 200, 950–965 (2013).
Hartman, G. & Danin, A. Isotopic values of plants in relation to water availability in the Eastern Mediterranean region. Oecologia 162, 837–852 (2010).
Chikaraishi, Y., Naraoka, H. & Poulson, S. R. Hydrogen and carbon isotopic fractionations of lipid biosynthesis among terrestrial (C3, C4 and CAM) and aquatic plants. Phytochemistry 65, 1369–1381 (2004).
Chikaraishi, Y. & Naraoka, H. Compound-specific δD-δ13C analyses of n-alkanes extracted from terrestrial and aquatic plants. Phytochemistry 63, 361–371 (2003).
Diefendorf, A. F. & Freimuth, E. J. Extracting the most from terrestrial plant-derived n-alkyl lipids and their carbon isotopes from the sedimentary record: A review. Org. Geochem. 103, 1–21 (2017).
Sachse, D. et al. Molecular paleohydrology: interpreting the hydrogen-isotopic composition of lipid biomarkers from photosynthesizing organisms. Annu. Rev. Earth Planet. Sci. 40, 221–249 (2012).
Craig, H. Isotopic variation in meteoric waters. Science 133, 1702–1703 (1961).
Gat, J. R. Oxygen and hydrogen isotopes in the hydrologic cycle. Annu. Rev. Earth Planet. Sci. 24, 225–262 (1996).
Brittingham, A. et al. Influence of the North Atlantic Oscillation on δD and δ 18O in meteoric water in the Armenian Highland. J. Hydrol. https://doi.org/10.1016/j.ympev.2009.07.024 (2019).
Magill, C. R., Ashley, G. M. & Freeman, K. H. Water, plants, and early human habitats in eastern. Africa. Proc. Natl. Acad. Sci. 110, 1175–80 (2013).
McInerney, F. A., Helliker, B. R. & Freeman, K. H. Hydrogen isotope ratios of leaf wax n-alkanes in grasses are insensitive to transpiration. Geochim. Cosmochim. Acta 75, 541–554 (2011).
Eley, Y., Dawson, L., Black, S., Andrews, J. & Pedentchouk, N. Understanding 2H/1H systematics of leaf wax coastal plants at Stiffkey saltmarsh, Norfolk, UK. Geochim. Cosmochim. Acta 128, 13–28 (2014).
Fine, P. M., Cass, G. R. & Simoneit, B. R. T. Chemical Characterization of Fine Particle Emissions from the Fireplace Combustion of Woods Grown in the Southern United States. Environ. Eng. Sci. 36, 1442–1451 (2002).
Fine, P. M., Cass, G. R. & Simoneit, B. R. T. Chemical Characterization of Fine Particle Emissions from the Fireplace Combustion of Wood Types Grown in the Midwestern and Western United States. Environ. Eng. Sci. 21, 387–409 (2004).
Fine, P. M., Cass, G. R. & Simoneit, B. R. T. Chemical Characterization of Fine Particle Emissions from the Wood Stove Combustion of Prevalent United States Tree Species. Environ. Eng. Sci. 21, 705–721 (2004).
Iinuma, Y. et al. Source characterization of biomass burning particles: The combustion of selected European conifers, African hardwood, savanna grass, and German and Indonesian peat. J. Geophys. Res. Atmos. 112 (2007).
Zhang, H. et al. Particle size distribution and polycyclic aromatic hydrocarbons emissions from agricultural crop residue burning. Environ. Sci. Technol. 45, 5477–5482 (2011).
Karp, A. T., Behrensmeyer, A. K. & Freeman, K. H. Grassland fire ecology has roots in the late Miocene. Proc. Natl. Acad. Sci. 115, 12130–12135 (2018).
Moritz, M. A. et al. Climate change and disruptions to global fire activity. Ecosphere 3, 1–22 (2012).
Daniau, A. L. et al. Predictability of biomass burning in response to climate changes. Global Biogeochem. Cycles 26, 1–12 (2012).
Joannin, S. et al. Vegetation, fire and climate history of the Lesser Caucasus: A new Holocene record from Zarishat fen (Armenia). J. Quat. Sci. 29, 70–82 (2014).
We thank P. Avetisyan and B. Yeritsyan, Institute for Archaeology and Ethnography, National Academy of Sciences, Republic of Armenia, for their continued support of our research in Armenia. We also thank the members of the Hrazdan Gorge Palaeolithic Project, including Beverly Schmidt-McGee for helping draft Figure 2. Travel funding for A.B. was provided by the University of Connecticut, Department of Anthropology Summer Research Fellowship. Funding to D.S.A. and K.N.W. for excavations at LKT1 was provided by the University of Connecticut’s Norian Armenian Programs Committee and the L.S.B. Leakey Foundation. Financial support for stable isotope analysis and PAH quantification to MTH was provided by ACS-PRF 56306-ND2 and NSF-EAR-1338256 and to A.B. by the Geological Society of America Graduate Student Research Grant. We thank the four anonymous reviewers who greatly improved this manuscript.
The authors declare no competing interests.
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Brittingham, A., Hren, M.T., Hartman, G. et al. Geochemical Evidence for the Control of Fire by Middle Palaeolithic Hominins. Sci Rep 9, 15368 (2019). https://doi.org/10.1038/s41598-019-51433-0
Fire as an Artifact—Advances in Paleolithic Combustion Structure Studies: Introduction to the Special Issue
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