Main

Our current understanding of Gigantopithecus blacki derives from Early to Middle Pleistocene cave deposits in southern China between the Yangtze River and the South China Sea (Fig. 1 and Supplementary Information section 1). This pongine7 is considered a key member of the Early to Middle Pleistocene GigantopithecusSinomastodon and Stegodon–Ailuropoda faunal zones of (sub)tropical oriental Asia, from about 2.0 million years ago (Ma) to 330 thousand years ago (ka)2,3,8,9. It is known for its unusually large molars, atypical enamel thickness, estimated body height of about 3 m and mass of 200–300 kg, making it the largest primate ever to have existed on Earth4. Despite 85 years of searching, the G. blacki fossil record is restricted to four mandibles and almost 2,000 isolated teeth with no postcranial evidence4. Its initial discovery in an apothecary shop in Hong Kong as a ‘Dragon tooth’1 initiated a search for the first in situ finds10 (Extended Data Fig. 1f) and culminated in the discovery of several cave sites in two main areas, Chongzuo and Bubing Basin, in the Guangxi ZAR province4. These sites contain crucial evidence for its survival and eventual demise.

Fig. 1: The location of the study sites in this research.
figure 1

ac, The location of Southern China, Guangxi ZAR province and the city of Nanning (a), with the location of the Chongzuo study area marked by a large box (b) and the Bubing Basin study area marked by a smaller box (c). b, The location of the 16 cave sites analysed in the Chongzuo study area. c, The location of the six caves analysed in the Bubing Basin study area including both G. blacki-bearing and non-G. blacki-bearing caves from both regions.

Very few of these G. blacki sites have been dated using more than one radiometric technique; thus the timing of extinction remains uncertain11. The current timeline for its presence is 2.2 Ma (Baikong cave12) to 420–330 ka (Hejiang Cave9). During this time, G. blacki underwent morphological changes including an increase in tooth size13 and dental complexity9, seemingly indicating a dietary change in response to ecological pressure13. Reconstructions of G. blacki diet based on the dental anatomy indicate a specialized herbivore with adaptations for the consumption of abrasive food14,15, heavy mastication of fibrous food16,17 and a fruit-rich diet6,18. The diverse forest ecosystem at the time of Baikong had the capacity to support the biomass of several primate communities4 over a wide area from Guangxi, Guizhou, Hainan and Hubei Provinces19. However, by the time of Hejiang, G. blacki had a dramatic range reduction to just Guangxi9,13. The reasons for this dramatic reduction and eventual extinction remain hotly disputed4 because of a lack of a regional approach, a focus on single sites and methods and an absence of behavioural4 and environmental evidence20.

To identify the potential causes of G. blacki extinction, we applied a regional approach to 22 caves in Chongzuo and Bubing Basin that contained either G. blacki-bearing (11) or non-G. blacki-bearing (11) cave deposits (Extended Data Figs. 1 and 2 and Supplementary Information sections 2 and 3). Using a combination of previous excavations (1999–2016) and newly discovered caves (2017–2020) we identified and sampled fossil breccias for dating, palaeoclimate proxies and behavioural analyses. We applied six independent dating techniques to the sediments (post-infrared-infrared stimulated luminescence (pIR-IRSL), optically stimulated luminescence (OSL), electron spin resonance (ESR) on quartz and U-series on speleothem) and fossils (U-series on teeth, coupled US-ESR) to determine a Bayesian modelled age range for each site (Supplementary Information sections 48), which were then further modelled to provide a regional extinction window (EW). We applied pollen, charcoal, palaeontological, stable isotope and microstratigraphical analyses to the sediments and fossils to reconstruct the past environments (Supplementary Information sections 3 and 1012). Finally, we applied trace element, stable isotope and dental microwear textural analysis (DMTA) to the G. blacki and closest relative Pongo weidenreichi teeth to determine any changes in the diet and behaviour of G. blacki before and within the EW that may have related to its demise (Supplementary Information sections 1214).

According to the 157 radiometric age estimates, the fossil evidence in the 22 caves ranges from 2,300 to 49 ka (Figs. 2a and 3a, Extended Data Figs. 36 and Supplementary Information sections 48 for all dating tables and discussion of limitations and uncertainties). This study expands the timeline for the presence of G. blacki from 2.3 Ma to 255 ka, provides a precise timing for the window of extinction at 295–215 ka (2σ) (Supplementary Information section 9) and establishes focus points for the palaeoenvironmental and behavioural analysis (pre-EW (2,300–700 ka), transitional phase (700–295 ka), EW (295–215 ka) and post-EW (215 ka to the present)).

Fig. 2: Example datasets to support the extinction events.
figure 2

ad, Data relate to timing (a), environment (b) and behaviour (c,d) presented by sites. a, Modelled age ranges of each cave (n = 22 caves) using the minimum and maximum age of the fossil-bearing unit (n = 157 samples). The caves (x axis) versus age (y axis), with G. blacki (green circles) and non-G. blacki (orange circles) breccia. The data points represent mean ages with s.d. at 2σ uncertainties. The insets are modelled breccia from Queque (i) and Baxian (ii). G, G. blacki-bearing breccia; F1, overlying flowstone; and Non-G, absence of G. blacki. Data points are mean ages with s.d. at 2σ uncertainties. The black horizontal rectangles (with dashed lines) represent the boundary according to the modelling (Supplementary Information section 2 and Supplementary Fig. S1a–v). The modelled EW is the vertical grey line. b, Percentage pollen from the sites in a representing arboreal (green), non-arboreal (yellow) and ferns (orange). The pie charts provide an average of pollen changes for pre- (left) and post-extinction (right). c, DMTA boxplot series according to age of 12 caves (x axis) versus molar microwear complexity (Asfc, top, y axis) and anisotropy (epLsar, bottom, y axis) of G. blacki (red, n = 16) and P. weidenreichi (blue, n = 22). The boxplots size ranges represent mean complexity and anisotropy values per site. Data are presented as mean values ± interquartile range and whiskers at 95% CI (Supplementary Table S28). d, Trace elemental mapping of G. blacki and P. weidenreichi. Sr/Ca (i) and Ba/Ca (ii) of a right M3 G. blacki tooth (CSQSN-44) and Sr/Ca map from a right M2 P. weidenreichi tooth (CSQ0811-4) (iii) all from Queque Cave. Below, Sr/Ca (iv) and Ba/Ca (v) from a P4 tooth of G. blacki (ST_02_109) compared to Sr/Ca (vi) from a left M3 tooth of P. weidenreichi (CLMST0911-118) all from Shuangtan Cave. a.u., arbitrary units.

Source Data

Fig. 3: A summary of all datasets plotted against time.
figure 3

a, Timeline for extinction based on the modelled age ranges for all 22 caves. The numbers on the y axis relate to the caves in Fig. 2a. Note the reduced timeline (1,800 ka). The EW (255 ± 40 ka) is a vertical grey box (EW) with a solid lighter grey box (transitional phase) for the start of increased environmental variability. b, The percentage pollen plotted on a timeline grouped into arboreal (green), non-arboreal (yellow) and ferns (orange). The darker strips represent sites that contain pollen data, whereas the lighter sections in between represent an estimation of pollen changes. The microcharcoal (black dashed line) correlates with the increase in ferns and decline in arboreal cover. The dark green arboreal sections represent forest disturbance/high turnover taxa such as Trema, Celtis and Sapindaceae are present during the transitional phase and EW. c, The percentage of G. blacki teeth (red) relative to P. weidenreichi teeth (blue) at representative caves as a rough proxy for the relative abundance of G. blacki in comparison to P. weidenreichi in each site. The relative number of G. blacki teeth declines just before the transitional phase representing a change in faunal composition and during the transitional phase representing the extirpation of G. blacki. d,e, Isotopic changes for fossil P. weidenreichi (blue circles and triangles) and G blacki (red circles and triangles) teeth plotted on a timeline; modern P. weidenreichi are blue squares. δ13C (‰) (d) and δ18O(‰) (e). f,g, DMTA boxplot time-series for microwear complexity (f) and anisotropy (g) of G. blacki (red) and P. weidenreichi (blue); see Fig. 2c for definitions. h, A landscape and environment timeslice demonstrating the change in vegetation and primate species from the pre-EW, through the EW to the post-EW.

Source Data

Our pollen analysis indicates that during the pre-EW the environment was dominated by arboreal species (Pinaceae, Fagaceae and Betulaceae) with patches of grassland (Figs. 2b and 3b). However, before the EW during the transitional phase there was a change in forest plant communities and an increase in forest disturbance taxa with more open forests dominating. Post-EW about 200 ka, there was a large decrease in arboreal cover, an increase in ferns (for example, Moraceae and Podocarpus), a large increase in grassland (for example, Poaceae) and increased evidence of charcoal in the landscape (Extended Data Fig. 7 and Supplementary Information section 10).

Detailed faunal analysis indicates that the pre-EW sites were characterized by G. blacki (in relatively large numbers) (Fig. 3c), Ailuropoda microta, Procynocephalus, Sinomastodon, Stegodon, Hesperotherium and Hippopotamodon, which shifted to G. blacki (in relatively small numbers) (Fig. 3c), Ailuropoda baconi, Stegodon and Elephas before the EW and an absence of G. blacki post-EW (Supplementary Information section 3). The microstratigraphic analyses of five caves show pre-EW microfacies dominated by fine grains, higher clays and oxides, bioturbation and guano-induced phosphatization. At the EW, grain sizes increased, with lower oxides, bioturbation and bone/tooth alteration enabling better fossil preservation. During the post-EW, this reverted back to pre-EW features (Extended Data Fig. 8c and Supplementary Information section 11).

The stable isotope data indicate that for the pre-EW period the δ13C and δ18O of G. blacki range between −16.2 to −13.8‰ and −9.7 to −7.0‰, respectively. During during the EW, this increases slightly to −15.3 to −10.3‰ and −9.3 to −6.3‰, respectively. In the case of P. weidenreichi, the pre-EW δ13C and δ18O ranges are similar at −14.7 to −13.7‰ and −7.1 to −6.3‰, extending to −14.7 to −13.3‰ and changing to −4.9 and −4.4‰ during the EW period (Fig. 3d,e, Extended Data Fig. 8b and Supplementary Information section 12).

The trace element analysis of the pre-EW G. blacki teeth shows several, distinct and synchronous Sr/Ca and Ba/Ca bandings in the enamel and dentine that change to significantly less visible diffuse banding closer to the EW (Fig. 2d, Extended Data Figs. 9 and 10a and Supplementary Information section 13). In addition, distinct lead banding can be seen in the pre-EW, which becomes less distinct during the EW (Extended Data Fig. 10a). The microwear analysis reveals no statistically significant dietary differences between G. blacki- and P. weidenreichi-bearing sites (Supplementary Information section 14). There are, however, significant dietary differences in four G. blacki-bearing sites between the pre-EW and just before the EW. G. blacki tends to show slightly higher fluctuations in mean anisotropy and complexity trend lines, whereas those of P. weidenreichi seem more stable, especially for anisotropy over and beyond the EW (Figs. 2c and 3f,g, Extended Data Fig. 10b and Supplementary Information section 14).

For the first time, the largest collection of in situ evidence of G. blacki spanning its entire range has been robustly dated to provide a precise timeline for the presence and absence of G. blacki from the fossil record. Previous dating has mostly focused on the earlier G. blacki evidence2,8 and site-specific chronologies (for example, ref. 9). In contrast, by constraining caves within the entire age range in both Chongzuo and Bubing Basin we have more accurately established a regional window of extinction at 295–215 ka.

The pollen and faunal data indicate that the early mosaic landscapes were interrupted by enhanced environmental variability (Fig. 3b) before the EW in the transitional phase as suggested by the change in forest communities and structures and post-EW as suggested by a decline in arboreal cover and an increase in ferns and grasslands associated with fire. This variability started in a stepwise manner between 1,100 and 350 ka, with dramatic increases from about 200 ka (Fig. 3b). We have interpreted this variability as shifts towards increased seasonality and drier environments, which caused a shift to seasonal subtropical/tropical moist lowland forests and an increase in shrubs and open grassland environments before and during the EW (Supplementary Information section 10). This environmental variability is also seen in the sedimentary record as the stable low-energy environments of pre-EW were replaced by unstable high-energy environments of the EW with water availability restricted to the wet seasons (Extended Data Fig. 8c and Supplementary Information section 11).

The decline in forest cover during this period is documented in China21, Southeast Asia22 and Australasia23. However, our pollen study demonstrates that the key to G. blacki extinction is not the deterioration in arboreal cover but rather the influence of environmental variability in changing the composition of forest communities, particularly the increase in disturbance taxa. Our stable isotope and trace element data provide new insights into the extent of this variability and the impacts on G. blacki (Supplementary Information sections 12 and 13). Pre-EW, G. blacki and P. weidenreichi both lived in closed canopy forested environments (Fig. 3b and Extended Data Fig. 8b), with stronger biogenic banding (Fig. 2d(i)–(iii)), probably reflecting a larger diversity of food sources, including seasonal fruits and flowers and periodic water consumption, as indicated by the clear lead banding (Extended Data Fig. 10a,b). The most likely food sources would have been in greater availability all year round causing only discrete stress in the population (Fig. 2d(i)–(iii)). With the exception of one individual, throughout the EW period G. blacki seems to have maintained a more specialized closed canopy niche, reliant on perhaps a mixture of forest plants (Extended Data Fig. 8b). This specialization during an environmental shift may have caused a more diffused biogenic signal in individuals’ dental tissue (Fig. 2d(iv)–(v)), thus suggesting a greatly reduced dietary diversity, less regular water consumption (Extended Data Fig. 10c,d) and increased chronic stress in the population (Fig. 2d(iv)–(v)). This is the first insight into the behaviour of G. blacki as a species on the brink of extinction, which is in stark contrast to P. weidenreichi (Fig. 2d(vi)) that shows much less stress at this time. Beyond the EW, P. weidenreichi seems to have shifted to exploit the more open, seasonal habitats (Extended Data Fig. 8b), perhaps continuing to exploit the seasonal masting of fruit as modern Pongo does in Borneo today24.

The changes in microwear values in G. blacki and P. weidenreichi teeth may also be linked to periods of fruit scarcity. G. blacki tends to show more specific dietary preferences (in both fruits and fibrous foods) indicating greater reliance on fibrous fall-back foods (Fig. 2c), such as over the EW when the climate became more seasonal and less fruits were available. This might have forced G. blacki to adapt its diet from higher nutritionally preferred components in lower supply to less nutritional fall-back foods in plentiful supply. The increased consumption of fibrous foods in P. weidenreichi over the EW may indicate a better switch to fall-back foods and an overall more flexible and balanced diet (Fig. 2c and Extended Data Fig. 10). This first DMTA analysis on the entire range of G. blacki material provides a unique insight into its inability to adapt and its potentially poor choice in fall-back foods.

Our study presents a precise timeline for G. blacki presence and extinction. During the pre-EW period, G. blacki flourished alongside other primates as a successful specialist (Fig. 3c), enjoying a large diversity of food in a rich evergreen-deciduous forest (Fig. 2d(i)–(ii)) and plentiful water sources (Extended Data Fig. 10a–d) within stable environmental conditions (Fig. 2b). Around 700–600 ka in the transitional phase, there was a shift towards increased seasonality causing a change in forest communities (Fig. 3b), less diversity in food sources (Fig. 2d(iii)–(iv)), unstable high-energy environments (Extended Data Fig. 8c), changes in the composition of the fauna and widespread faunal turnovers (Fig. 3c and Supplementary Information section 2), a shift towards seasonal habitats by P. weidenreichi (Extended Data Fig. 8b) and a shift in the dietary diversity and behaviour of G. blacki (Figs. 2d and 3f,g).

Despite sharing similar environments with P. weidenreichi pre-EW, from 600 to 300 ka there is evidence of the inability of G. blacki to adapt to this transitional period, which had a greater impact on its resilience to the changing ecology. The reliance of G. blacki on fruits and lower nutritious fall-back foods (Fig. 2c) created a higher-risk foraging strategy and, combined with its much larger, less mobile body size made it more vulnerable to changes in forest structures25 (Fig. 2c). Moreover, G. blacki was exclusively terrestrial, possibly with a small geographic range20 but periodically travelled down the valley for water consumption (Extended Data Fig. 10a–d), whereas P. weidenreichi was more arboreal, mobile and semisolitary collecting water in the leaf canopy. Furthermore, the unique dentognathic features13,14 and giant body size4,5 of G. blacki suggest a higher demand in food uptake and slower and more delayed growth pattern, which may imply a lower reproduction rate26. Although G. blacki increased in tooth size over the Pleistocene, implying an increase in body size also, P. weidenreichi decreased27 making it a more agile adaptor. P. weidenreichi also demonstrated a flexibility towards the open habitats (Extended Data Fig. 8b) potentially moving in smaller groups and was able to adjust its behaviour in response to the environmental variability, causing a less stressed population (Fig. 3d).

By about 300 ka there is evidence of a struggling G. blacki population as the number of G. blacki caves and teeth reduced (Fig. 3c), indicating a dwindling population. The stark change in the teeth banding of G. blacki indicates chronic stress in the population (Fig. 2d(iv)–(v)) and changes from its preferred dietary behaviour (Fig. 2c and Extended Data Fig. 10f,g) indicate that G. blacki was struggling to respond to the environmental changes on a potentially shrinking territory20. It would seem that its forest refugia changed its structure and became too open and disturbed for this species to sustain itself. When compared to other well-known extinction events in North America and Australia influenced by Homo sapiens28,29,30, there is no evidence to suggest that archaic hominins played a role in this earlier megafaunal extinction event in southern China.

Presenting a defined cause for extinction is a feat that has seldom been achieved for many extinct species as it requires a genus- and species-specific approach28. Although determining the exact drivers of megafaunal extirpation and extinction can be highly challenging29,30, our multiproxy record of G. blacki timing, environment and behaviour provides robust regional insights into the ecological context of this species. G. blacki was the ultimate specialist and, when the arboreal environments changed, its struggle to adapt sealed its fate. In comparison, the generalist Homo extended and diversified across Southeast Asia during this period and seemed to have flexibly exploited the new mosaic environments that posed such a problem to G. blacki. Overall, our dataset provides important context for the changing fortunes of different primate species in Southeast Asia, shedding new light onto the demise of the largest primate ever to have roamed the planet.

Methods

Speleology and excavation techniques

Caves were discovered using a combination of local knowledge, field survey, drone mapping surveys and targeted reconnaissance with a dedicated caving team. Excavation grids were set up on the basis of the shape of cave passages and distribution of fossil-containing deposits. Jackhammers were used to break blocks of fossil-breccia and the fossils were extracted using geological hammers. Fine cleaning, identification and cataloguing were conducted in the Institute of Vertebrate Paleontology and Paleoanthropology (IVPP) laboratories.

Luminescence dating with pIR-IRSL/SG quartz

Large bulk samples of the fossil-bearing breccia were sampled in situ under subdued red-light conditions from each cave site (Supplementary Fig. S1a–v) and processed using the standard sample purification procedures for quartz and feldspar separation including a 40% and 10% wash in hydrofluoric acid for 45 and 10 min, respectively31. All luminescence analysis was conducted at the ‘Traps’ luminescence dating facility at Macquarie University in Sydney, Australia. Single aliquots of 90–125 µm feldspar and 180–212 µm single grains (SGs) of quartz or feldspar were processed in a Riso TL-DA-20 containing an automated DASH set up with a dual laser single-grain attachment and a blue/UV sensitive photomultiplier tube (PDM9107Q-AP-TTL-03) using either the blue filter pack (Schott BG-39 (2 mm) and Corning 7-59 (4 mm) filters for feldspar or U340s (2× Hoya U340 3.5 mm) for quartz. Feldspar equivalent doses were corrected according to the results of the anomalous fading tests (using a weighted mean fading rate of 2.0 ± 0.2% per decade)32 but no residual corrections were undertaken and both feldspar and quartz Des were then run through a minimum age model33 to identify the population that had the most bleaching before burial.

Measurements of 238U, 235U, 232Th and 40K were estimated using Geiger-Muller multicounter beta counting and thick source alpha counting of dried and powdered sediment samples in the laboratory, combined with in situ gamma spectrometry in the field. The corresponding (dry) beta and gamma dose rates were obtained using the conversion factors of ref. 34 and the beta-dose attenuation factors of ref. 35. Cosmic-ray dose rates were estimated from published relationships36, making allowance for the sediment overburden at the sample locality (ranging from 3.99 to 0.20 m), the altitude (ranging from 2,000 to 176 m above sea level) and geomagnetic latitude and longitude of the sampling sites.

U-series dating of teeth

A total of 22 G. blacki and 9 P. weidenreichi sp. fossil teeth were analysed for U-series dating. Uranium series measurements were undertaken by laser ablation combined with multicollector inductively coupled plasma mass spectrometer (MC-ICP-MS) at GARG-SCU according to protocols in ref. 37. Laser ablation was performed with a New Wave Research 213 nm laser and thorium (230Th, 232Th) and uranium (234U, 235U, 238U) isotopes were measured on a Thermo Neptune XT MC-ICP-MS. Teeth were ablated using rasters of 5 min each and were measured with standards before and after.

Coupled US-ESR dating of teeth

Enamel fragments from each tooth dated by coupled US-ESR techniques were separated using a hand-held diamond saw following the protocol developed by ref. 38. Fragments were then measured at room temperature on a Freiberg MS5000 ESR X-band spectrometer at a 0.1 mT modulation amplitude, ten scans, 2 mW power, 100 G sweep and 100 KHz modulation frequency. Each fragment was irradiated, following exponentially increasing irradiation times. Sediment elemental concentrations, external beta and gamma dose rate contributions and water content were obtained from in situ measurements. The external beta-dose rates have been extrapolated from the U, Th and K contents measured on a portion of sediment subsample (about 8 g). The external gamma dose rates were determined using a portable gamma spectrometer at each site.

ESR dating of quartz

A total of seven samples of purified quartz (previously prepared at Macquarie University) were analysed for ESR dating purpose. For a couple of them (CBAK10 and CZW2), two grain-size fractions were measured. Quartz grains were dated by means of the multiple aliquots additive dose method and following the multiple ventre approach initially proposed by ref. 39. In each sample, the ESR signals of both the aluminium (Al) and titanium (Ti) centres were either acquired in separate spectra using specifically optimized parameters (standard CENIEH procedure, for example, ref. 40) or in a single spectrum (for example, ref. 41). Gamma irradiations and ESR measurements were performed at the National Research Centre on Human Evolution (CENIEH), Spain, using a Gammacell-1000 and an EMXmicro 6/1Bruker X-band ESR spectrometer, respectively.

U-series dating of carbonates

Separate subsamples were drilled from the fresh cross-section of a hand specimen of the in situ flowstone using a hand-drill. The powdered subsamples were subjected to chemical treatment and isotopic measurements by mass spectrometry42. U-series dating of most speleothem samples was conducted in the Radiogenic Isotope Facility (The University of Queensland) using a Nu Plasma MC-ICP-MS. Analytical procedures followed previous publications for MC-ICP-MS43,44,45. 230Th/234U ages were calculated using Isoplot EX 3.75 (ref. 41) and half-lives of 75,690 years (230Th) and 245,250 years (234U)46. Analyses were also undertaken by laser ablation MC-ICP-MS at the Wollongong Isotope Geochronology Laboratory, University of Wollongong47. Laser ablation was performed with a New Wave Research ArF 193 nm Excimer laser, equipped with a TV2 cell.

Modelling

To evaluate the uncertainties of the integrated dating approach to the site (Supplementary Tables 14), Bayesian modelling was performed on all independent age estimates using the OxCal (v.4.4) software 52 (https://c14.arch.ox.ac.uk/oxcal.html)48. The analyses incorporated the probability distributions of individual ages, constraints imposed by stratigraphic relationships and the reported minimum or maximum nature of some of the individual age estimates. Each individual age was included as a Gaussian distribution (with mean and s.d. defined by the age estimate and their associated uncertainties) and the resulting age ranges for each unit were presented at 1σ. The code used for each site is publicly available in Zenodo (10.5281/zenodo.10077255). 

Pollen analysis

Pollen analysis followed a modified standard methodology described by ref. 49, in which sediment was dispersed in Calgon (3%) treated with HCl (10%) and sieved at >125 µm, allowed to settle in HL (heavy liquid/LST-lithium heteropolytungstates) at a density of 2.01 SG and centrifuged, then acetolysis which removes cellulose and stains the pollen followed. The remaining sample was then mounted on slides with glycerol. Pollen identification was aided by the Australasian Pollen and Spore Atlas (online resource50) and a handbook of quaternary pollen and spores in China51. Macrocharcoal analysis followed the methodology outlined by ref. 52.

Microstratigraphy and spectroscopy

Five intact cave blocks were sampled for the purposes of a range of synergistic microcontextualized analyses. First, a microstratigraphic study was undertaken using petrographic microscopy (for example, refs. 53,54,55). Sediment blocks were prepared at the Flinders University Microarchaeology Laboratory and ten glass thin sections (76 mm × 50 mm × 30 µm) were made by Adelaide Petrographics. Thin sections were analysed using a Leica DM2700 P (Wetzlar) polarizing microscope following the terminology of ref. 56. Alkalinity (pH), X-ray diffraction (XRD)57,58 in an Aeris Malvern Panalytical benchtop X-ray diffractometer (2018, The Netherlands) and X-ray fluorescence (XRF)59,60 in an Axios Malvern Panalytical WD-XRF spectrometer tests were applied to the microsampled bulk sediments subsamples at Macquarie University.

Stable isotope analysis

A total of 27 teeth (15 fossil G. blacki and 7 fossil and 5 modern P. weidenreichi teeth) were cleaned using an air abrasion system. Enamel powder for bulk analysis was obtained using a diamond-tipped drill. All enamel powder was pretreated following established protocols23,61. Following reaction with 100% phosphoric acid, gases evolved from the samples were analysed for their stable carbon and oxygen isotopic measurements using a Thermo Gas Bench 2 connected to a Thermo Delta V Advantage Mass Spectrometer at the Max Planck Institute for Geoanthropology (formerly for the Science of Human History). The δ13C and δ18O values were compared against International Standards. Overall measurement precision was studied through the measurement of repeat extracts from a bovid tooth enamel standard (n = 30, ±0.2‰ for both δ13C and δ18O values).

Trace element analysis of teeth

Fossil teeth were sectioned with a high-precision diamond saw and polished to more than 10 µm smoothness. Laser ablation ICP-MS was used for trace elemental mapping analyses of the samples according to the published protocol from ref. 62. The GARG facility at Southern Cross University uses an ESI NW213 coupled to an Agilent 7700 ICP-MS, using rastered laser beams run along the sample surface in a straight line. A laser spot size of 40 μm, a scan speed of 80 μm s−1, laser intensity of 80% and a total integration time of 0.50 s were used to produce data points.

DMTA

DMTA was applied to facet 9, as close as possible to the (ante mortem) tip crushing point of moderately worn (wear stages 2 to 4; ref. 63) first (m1), second (m2) and third (m3) lower molars of extinct G. blacki (n = 16), extinct P. weidenreichi (n = 22) (IVPP) and extant P. pygmaeus (n = 3) (South Australian Museum). Sample size was restricted by fossil availability. Cleaning, moulding with polyvinylsiloxane and casting with epoxy resin followed standard DMTA procedures64,65,66,67,68. Scanning of 242 × 181 μm2 areas was conducted on a Sensofar PLμ neox confocal profiler at the Flinders University Palaeontology Microscopy facility. Axonometric digital elevation models were fabricated in SensoMAP Premium 8.2.9564 following the ‘soft filter procedure’68 and analysed with the embedded scale-sensitive fractal analysis module. Statistical analyses and data visualization were carried out in Minitab 19.2020.1 and R Studio 1.4.1717.

Reporting summary

Further information on research design is available in the Nature Portfolio Reporting Summary linked to this article.