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# A new hypothesis for the origin of Amazonian Dark Earths

## Abstract

Amazonian Dark Earths (ADEs) are unusually fertile soils characterised by elevated concentrations of microscopic charcoal particles, which confer their distinctive colouration. Frequent occurrences of pre-Columbian artefacts at ADE sites led to their ubiquitous classification as Anthrosols (soils of anthropic origin). However, it remains unclear how indigenous peoples created areas of high fertility in one of the most nutrient-impoverished environments on Earth. Here, we report new data from a well-studied ADE site in the Brazilian Amazon, which compel us to reconsider its anthropic origin. The amounts of phosphorus and calcium—two of the least abundant macronutrients in the region—are orders of magnitude higher in ADE profiles than in the surrounding soil. The elevated levels of phosphorus and calcium, which are often interpreted as evidence of human activity at other sites, correlate spatially with trace elements that indicate exogenous mineral sources rather than in situ deposition. Stable isotope ratios of neodymium, strontium, and radiocarbon activity of microcharcoal particles also indicate exogenous inputs from alluvial deposition of carbon and mineral elements to ADE profiles,  beginning several thousands of years before the earliest evidence of soil management for plant cultivation in the region. Our data suggest that indigenous peoples harnessed natural processes of landscape formation, which led to the unique properties of ADEs, but were not responsible for their genesis. If corroborated elsewhere, this hypothesis would transform our understanding of human influence in Amazonia, opening new frontiers for the sustainable use of tropical landscapes going forward.

## Introduction

Discovered decades ago in central Brazil1, Amazonian Dark Earths (ADEs) are now regarded as a Pan-Amazonian anthropological phenomenon2. The exceptional fertility of ADEs, combined with a high concentration of pyrogenic carbon3, and frequent observations of pre-Columbian artefacts led to their ubiquitous classification as anthropic soils4, often referred to as Pretic Anthrosols5. The current paradigm of ADE formation postulates that pyrolysis of nutrient-rich biomass created hundreds of high-fertility patches (some as large as 350 hectares)4 surrounded by the acidic dystrophic soils6 that covers most of the Amazon basin7. However, neither the timing nor the magnitude of human occupation needed for ADE formation is well-defined. Among key questions that remain unanswered is how indigenous populations—subsisting from incipient agriculture, aquatic wildlife, and hunting—created persistent areas of high fertility in the notoriously nutrient-impoverished Amazon basin?

Amazonian landscapes are dominated by highly weathered Oxisols and Ultisols, which are characterised by high acidity and low nutrient concentrations. As in other parts of the tropics, native plant species display adaptations, such as nutrient uptake from litter and tolerance to elements that are toxic for crop species8,9,10, which allow Amazonian soils to maintain some of the most productive ecosystems on Earth while limiting food production even under intensive management11. Recent findings suggest that domestication of native plant species dates back to >10,000 years ago in western Amazonia12, with the emergence of complex societies that relied on soil management for agriculture occurring <4000 years ago13. Some of the earliest evidence of sedentary settlements in Amazonia comes from the Peruvian Andes, where records of deforestation and soil erosion exist for much of the past 6900 years14. For most of the Amazon basin, however, the earliest evidence of intensive cultivation (inferred from pollen data) falls between 3380 and 700 years ago15. Notably, ADEs are rare near Andean settlements16 and the vast majority of ADE sites are found thousands of kilometres away in the central and eastern Brazilian Amazon17, where evidence of management is even more recent (2500–500 years ago).

The existence of small and scattered ADE patches (<1–2 ha) in central and eastern Amazonia is often attributed to transient communities containing few people over a long time. By contrast, larger ADE patches are thought to have been created by people living in large sedentary villages18. Informed by anthropological studies, we sought to develop new evidence from well-studied ADE sites, which is thought to have originated from a large settlement <2000 years ago (Fig. 1). The site is home to the Brazilian Agroforestry Research Station (EMBRAPA – CPAA), where the local ADE has been classified as a typical Anthrosol. As in other ADEs, archaeological artefacts are found in charcoal-rich soil layers in which pyrogenic carbon is 5–10% of the total carbon pool, and where vestiges of human faeces are also present19. It is clear that pre-Columbian land-use occurred in our region, but it remains unclear how ancient (or modern) soil management can create such areas of high fertility. The current view of ADE genesis suggests that the artefacts found in nutrient- and charcoal-rich Pretic horizons result from biomass burning and application to the soil. This view has fuelled an entire industry of charcoal production from biomass (i.e. biochar) in which ADEs are described as a model for sustainable agriculture20. Under experimental application, however, biochar alone (or in combination with fertilisers) has proved inadequate to replicate basic characteristics of indigenous ADEs, such as their long-lasting mineral fertility21,22,23. This reveals a lack of understanding that warrants further investigation into the genesis of ADEs.

To improve understanding of ADE formation, we used EMBRAPA’s reference profiles across a contiguous patch of ~12 ha to select ~4.5 ha for intensive sampling in a paired scheme that provides maximum contrast among ADE and adjacent Ultisols. All intensively sampled soils were under dense secondary evergreen rainforest (>12 m canopy height), which had not been managed for at least 40 years since the research station was established. Across the study area, we measured mineral nutrient excess in ADE to estimate the input necessary to explain its origin. As a proxy for the overall amount of mineral nutrient input, we focused on phosphorus (P) and calcium (Ca) excess, which are two of the most limiting elements in tropical landscapes24,25,26. We then quantified the association of P and Ca excess with the concentration of trace elements, including strontium (Sr) and neodymium (Nd), which serve as proxies for mineral source. Previous research showed a direct relationship between the amount of charcoal and the colour of ADEs at our site, where microscopic charcoal (<500 μm) comprises most of the pyrogenic carbon pool, and pretic horizons are dominated by very small particles (<40 μm)5. Building on those findings, we determined the source and timing of microcharcoal deposition using stable carbon isotope ratios and calibrated radiocarbon (14C) dates of ADE and Ultisol samples. Finally, we analysed carbon and nutrient data in light of the local anthropological context to estimate the chronology of management and the population density needed to attain the observed gain in ADE fertility. Our results show that large sedentary populations would have had to manage soils thousands of years prior to the emergence of agriculture in the region or, more likely, that indigenous peoples used their knowledge to identify and preferentially settle areas of exceptionally high fertility before the onset of intensive land use in central Amazonia.

## Results and discussion

### Nutrient budget

A spatial interpolation analysis using nutrient concentrations from reference soil profiles (Fig. 1) was used to determine the sampling effort for the determination of total nutrients and stocks. A map of extractable concentration was used to guide the determination of total P and Ca stocks. Extractable P and Ca concentrations were 1–3 orders of magnitude greater within the ADE patch than in the surrounding Ultisol (Fig. 2). The well-defined spatial pattern of extractable P and Ca from the most fertile ADE profiles (blue) to nutrient-depleted Ultisols (red) guided an in-depth characterisation of elemental and isotopic composition performed along six transects ~100 m apart from one another, each containing 5 soil profiles, ~10 m apart from one another, for a total of 30 intensively sampled profiles (blue diamonds). Those profiles yielded samples for a maximum contrast comparison—that is, highest and lowest soil fertility along the site’s southwest–northeast axis—on the basis of total nutrient stocks between ADEs and reference Ultisols (red triangles, Fig. 3).

To estimate total nutrient stocks, bulk density was multiplied by Ca and P concentrations at 10 cm depth increment up to 1 m in each profile. Without exception, all sampled profiles showed much larger nutrient stocks (expressed as megagrams per hectare; Mg ha−1) in the ADE than in the surrounding soil. On average, we found that ADE profiles contain 16.8 Mg P ha−1 and 14.9 Mg Ca ha−1 in excess relative to the surrounding Ultisol (Fig. 3). Outside the ADE patch, the stocks of P and Ca are as low as those typically reported for other Brazilian Oxisols and Ultisols27. Inside the patch, the stocks of P and Ca are similar to those found in other ADEs28 and higher than typical values for agricultural and timber production systems under systematic nutrient addition29. Notably, neither the elemental stoichiometries of freshwater fish (Ca:P ~2.13)30 nor human faeces (Ca:P ~2)31 are apparent in ADE profiles and differences in fertility go beyond those two macronutrients. Concentrations of 16 mineral elements were significantly greater in ADE than in Ultisol profiles in paired t-tests: Ba, Ca, Cd, Co, Cs, Cu, K, Li, Mg, Mn, Ni, P, Rb, Sr, Tl, and Zn (p < 0.05; Supplementary Table 1). Most chemical parameters, including trace elements, were positively correlated with P and/or Ca with a strong clustering within the Ultisols but much variability within ADEs (Principal Component Axis 1 explained ~56% of the variance in elemental composition clustered by soil type; Supplementary Fig. 1). On the other hand, a weak clustering by depth was observed with a similar range of variation for ADEs and Ultisols (Principal Component Axis 2).

### Exogenous inputs

We found a small but significant difference in total carbon concentration (<5 g kg−1) between ADE and Ultisol profiles near the soil surface (0–30 cm depth), but that difference disappeared at greater depths (80–100 cm; Fig. 4). Nutrient-rich dark-coloured profiles have high pyrogenic carbon concentrations 5- to 10-fold higher than those found in Ultisols. Stable carbon isotope ratios indicate typical forest biomass input to Ultisols, whereas C4 grasses contributed 5–19% of total carbon to ADE horizons (30–100 cm). The isotopic enrichment of ADE carbon profiles coincides with microcharcoal inputs, beginning ~7630 ± 80 years ago (Fig. 5), with a clear offset between forest organic matter (Ultisols) and enriched δ13C ratios (ADEs). The earliest input of microcharcoal to ADEs pre-dates the earliest evidence of land management in the region and falls within a period of expansion for C4-dominated grasslands in the Solimões Basin (~20,000–7500 years ago)32. Importantly, our 14C dates represent the most recent of a range of possible ages because inputs from human activity, as well as natural processes, may have contributed additional charcoal into the soil matrix. Although more recalcitrant and significantly older than bulk organic matter, charcoal is degradable and can be transformed from macro to micro particles under continued disturbance23. This could explain the accumulation of microcharcoal at intermediate depths and implies that the earliest input events identified here are, in fact, significantly older. We posit that the timing of the formation of other ADEs would be pushed back significantly following a detailed analysis of microcharcoal deposition.

Human activity could have influenced the δ13C values both indirectly (through the removal of trees) and directly (through the introduction of C4 crops such as maize). However, previous studies yielded no evidence of grass or Maize phytoliths at our site5. The nearest area where fossil Maize pollen is found (~600 linear kilometres to the East of our site) sets the earliest evidence of cultivation ~4000 years ago15, which is consistent with the emergence of cultivation in other areas of the Amazon basin33,34,35. Therefore, we can rule out agriculture as the source of C4-derived carbon input at the onset of ADE genesis. In some areas of the western Amazon, charcoal and pollen records suggest human use of fire ~6500 years ago36, but in ADE sites of central and eastern Amazon, land management is thought to be much more recent. On the other hand, a synthesis of charcoal and pollen records suggest a shift from well-drained to flooded conditions (signalling the formation of lakes) before the apex pre-Columbian activity in our region37. At our site, markedly different elemental signatures of ADE and Ultisols indicate different flood regimes in the past with elevated concentrations of mineral elements observed near a geomorphic feature that we interpret as a natural levee. The trace elements (e.g. Ni, Rb, Ti, Zn) found at the same depths in which we see enriched P, Ca, and charcoal levels match what might be expected from alluvial deposition and suggest major exogenous inputs to ADE profiles but not to the surrounding Ultisol (Supplementary Table 1). This implies that two critical ingredients needed for ADE formation (microcharcoal, which confers it’s colour and cation-exchange capacity; and mineral elements, which are in extremely low supply in the surrounding soil) were deposited before soil management and plant cultivation took place.

The timing and magnitude of charcoal and nutrient accumulation at our site match those found in sedimentary deposits that can be traced to open vegetation fires upstream, on the basis of 14C dates and δ13C signatures38. Paleoflood archives (soil biogenic silica)39 and records of monsoon intensity (speleothem oxygen and strontium isotope ratios)40, 41 indicate a climate-driven shift in river dynamics following a persistent dry period (~8000–4000 years ago)42, which is thought to have reduced fire disturbance, causing a regional increase in tree cover, well into the late-Holocene43. The resulting changes in vegetation cover could have caused divergent patterns of carbon and nutrient accumulation in flooded versus non-flooded areas44, consistent with ADE and Ultisol differences at our site. Many areas of central Amazonia today are associated with sediment deposits representative of flood regimes that were either deactivated during the Holocene or are presently in the process of deactivation when sedimentary deposits become suitable habitats for grasslands within the rainforest45. The abundance of C4-derived microcharcoal (19% of the total organic carbon pool) in deep ADE layers and the absence of in situ records of C4 species—combined with the fact that fire frequency, charcoal production, and nutrient losses are much higher in open savannas than in rainforests27, 29, 46—suggest that pyrogenic carbon and nutrients were transported to our site from C4-dominated landscapes upstream. Indeed, the majority of soil properties observed here could be explained by mid- to late-Holocene flood events39, possibly triggered by increased monsoon intensity41, which are thought to have affected fire regime and vegetation cover throughout the region43. In all likelihood, such natural processes would have also contributed to the formation of other ADEs throughout the region, which could explain why a highly predictable pattern of ADE distribution emerges from maximum entropy models based solely on geomorphological parameters, such as distance from rivers and elevation17.

Isotope ratios of the mineral soil fraction also indicate fluvial inputs to the ADE soil. We found that ADE horizons are less radiogenic (p < 0.05) in Sr and more radiogenic in Nd and εNd(0) (Fig. 6). Differences with soil depth were significant for Sr isotope ratios reflecting greater solubility47 relative to Nd. The ADE Sr isotope signature (0.714) falls between those of the Solimões River at a nearby site (0.709, constant through the year) and the Ultisols (0.7152)48. Similarly, εNd(0) signature of the ADE falls between the values for Solimões River and its headwaters and the value for the Ultisols. This result is consistent with the geomorphic setting of the site, which indicates an alluvial contribution of nutrients to the site in the past. A continuous bluff, which we interpret as a natural levee (Fig. 1), is visible at the southwestern limits of the ADE patch. At the levee, the best estimate of terrain height is a maximum of 27 m above the modern average river water level (~10 m above the adjacent floodplain; Fig. 7). Although above flood limits today, the site is at an elevation known to have been inundated in the early Holocene and possibly into the middle Holocene49. We do not expect a significant contribution from the modern river water or water table because Sr and Nd are mainly found in the mineral phase. The concentration of Sr dissolved in river waters in the Amazon is in the order of parts per billion, whereas the Sr concentration in suspended sediments is on the order of parts per million48, and Nd is often below detection limits in river water50. Thus, variation in Sr and Nd values were in all likelihood caused by fluvial mineral deposition that led to terrace development, which we interpret as the local manifestation of regional paleo floods identified in several other depositional sites51,52,53.

Further support for the fluvial influence on the ADE soils is provided by differences in particle size distribution. Specifically, the classification of ADE profiles as sandy clay loam and adjacent Ultisols as very clayey has been tentatively attributed to the fusion of clay and organic matter into sand-sized particles by fire5. Our data point to a more parsimonious explanation; that is, alluvial deposition changed nutrient and particle size profiles at the site. As a first approximation, radiogenic signatures indicate that ~24% of Sr mass in ADE profiles originate from either fishbone or river sediment (Eq. 3), as both sources have the same Sr isotopic composition54. It is important to note that the Sr/Ca ratio in fishbone (0.004) is much lower than in river suspended sediments (0.02). Assuming a concentration of Sr in the soil of 200 mg kg−1 and in fishbone of 400 mg kg−1, the final Ca concentration of the mixture would be about 10 times higher than that of Sr, which is approximately what we see in our results. Similarly, the Nd mixtures indicate riverine inputs with significant differences between ADE and Ultisol, albeit with larger deviations from the mean (Fig. 6). Clay mineralogy characterisation using X-ray diffraction showed no differences in the type of dominant clays found in ADE and Ultisol profiles (Supplementary Fig. 3), but that can be explained by two factors. First, across the alluvial plain of the Solimões-Amazon River, optically stimulated luminescence and geomorphological data show large fluvial features of weathered sediment deposited at the Pleistocene-Holocene boundary55 (long before the deposition of carbon and nutrients described above). Second, no neo-formation of minerals is expected for the highly weathered assemblages (e.g. kaolinite and iron/aluminium oxides, such as goethite) that are abundant in river sediments of this section of the Amazon basin56. Thus, it is not surprising that clay mineralogy is the only measured variable to converge between ADE and Ultisol.

Taken together, our findings underscore the need for a broader view of landscape evolution as a path towards understanding ADE formation and redirecting applications for sustainable land use and conservation, such as those arising from biochar research. Other ADEs should be investigated for a potential alluvial origin, on the basis of physical properties and elemental sources, to improve basic knowledge of the transition from nomadic to sedentary populations in Amazonia and their influence on socioecological trajectories.

### Human inputs

In pre-Columbian times, the most likely human-derived nutrient inputs to soil were food waste and faeces. Archaeologists hypothesise that such domestic waste deposits led to the widespread formation of anthropic soils near ancient settlements18, in a process that some authors have described as non-intentional57. Molecular markers of human faeces found in several ADEs, including our site19, offer support for that hypothesis. However, we still do not know how much waste would have been needed to form a typical ADE patch. Here, we offer a first approximation based on the excess amount of P and Ca, calculated in relation to the surrounding Ultisol at our site (~32 Mg ha−1; Fig. 3), which implicitly represents the depositional history of many other elements that correlate strongly with those macronutrients (Supplementary Fig. 1).

A synthesis of anthropological studies from riverine areas where ADEs are typically found indicates population densities ranging from 20 to 60 people per hectare in sedentary villages in 1492 AD and suggest that at least five million people inhabited the Amazon region prior to European contact58. Those estimates fall within the range of dense pre-Columbian landscapes elsewhere in the Americas. For example, in 1519 AD the Aztec empire was comprised of several million people, living in city-state capitals with a median density of 50 people per hectare62. Population estimates can have large margins of error and should not be used to generalise patterns across the region. The Amazon basin has a complex history of occupation and land use and, prior to European contact, indigenous peoples relied on >80 different plant species associated with settlements that possibly covered 0.1% of the region63. A recent analysis of cultural transitions suggests that specialised land-use systems faced major reorganisation during Holocene climate fluctuations discussed above, whereas others that relied on polyculture agroforestry were more resilient and remained largely unaffected64. Our analysis of elemental amounts and sources is site-specific and it is not intended to capture regional socioecological transitions, but the clear picture emerging from our data is that indigenous populations identified and actively used ADEs after their genesis. It is possible that dense populations occupied riverine areas uninterruptedly for thousands of years longer than previously recorded, contributing large amounts of fish waste to the soil, as it appears to have been the case for some of the first hunter–fisher–gatherer communities in western Amazonia65. It is also possible that those communities were capable of recycling nearly all of their waste into ADEs, with little to no loss through leaching or burning. It is more plausible, however, that human-derived inputs represent a minor fraction of ADE’s chemical makeup, a fraction that, we hypothesise, was introduced in the relatively recent past. If our hypothesis holds true, other sites will exhibit similar depositional patterns and biogeochemical signatures as those reported here.

### Final considerations

We found direct and indirect evidence that natural processes created a well-studied ADE site in the Brazilian Amazon. Our data reveal external inputs of carbon and mineral elements several thousands of years earlier, and in several orders of magnitude greater amounts, than those expected from human activity. Across the Amazon basin, three main phases of human occupation are thought to have occurred: a pre-cultivation period (>6000 years ago); an early-cultivation period (6000–2500 years ago); and a late-cultivation period (2500–500 years ago)15—a chronology of occupation that is supported by genomic, linguistic, and archaeological evidence66. At our site, the enrichment of microcharcoal and mineral elements (two critical ingredients needed for ADE formation) began at ~7630 years ago, that is, before the earliest evidence of soil management that characterizes the late-cultivation period. To achieve the observed levels of P and Ca enrichment at the site, large human populations would have had to actively manage soils continuously for thousands of years prior to the currently accepted chronology of sedentarisation. A more parsimonious explanation is that indigenous peoples used their knowledge to identify and preferentially settle areas of high fertility before the emergence of plant cultivation. This hypothesis implies that pre-Columbian societies understood and exploited natural processes of landscape formation, which led to the unique properties of ADEs, but were not responsible for their genesis. Our findings do not preclude, however, a more recent human effect on the local environment. The wisdom of native populations, manifested for example in the well-documented recent application of waste materials to the soil, may well have further enriched ADE profiles or, at least, countered their otherwise-inevitable degradation. The extent to which other ADE sites originated from natural depositional processes or were managed for long-lasting fertility remains unclear. New discoveries are to be expected from interdisciplinary research that combines indigenous knowledge with biogeochemical and geographical data to study landscape development as a path toward sustainable land use in the Amazon and other tropical environments.

## Methods

### Site description and sampling scheme

The EMBRAPA-CPAA site covers 210 hectares of managed and unmanaged land just north of the Solimões River near its confluence with the Negro River, within the sedimentary basin of the Amazon River. Satellite and field measurements show that the terrace is located ~40 m above the modern sea level, at a maximum of ~27 m above the modern river level, or ~10 m above the adjacent floodplain (3° 15′ 6.8″ S and 60° 13′ 46.9″ W). The relative topographic positions of ADE and Ultisol at the site matches the classic bluff model of prehistoric riverine settlement (close to the river and with fresh sediment providing enhanced fertility)67. A bluff is indeed visible at the southwestern limits of the ADE patch, which is interpreted as a natural levee formed due to Holocene paleo river dynamics (Fig. 1). This interpretation is based on other features of the Solimões-Amazon fluvial system, between the Negro and Madeira tributaries. Specifically, records of paleo river dynamics in many extensions of the Solimões River indicates that the combined action of neotectonics and rainforest establishment related to the increase of humidity in Amazonia ~6000 years ago allowed for sediment accumulation and asymmetric distribution of fluvial terraces throughout the region53.

Lidar data was not available for the study area, but the comparison of NASA’s SRTM and nearby ICESAT-2 satellite data show with no systematic offset, where blue colours below 30 m are within the 100-year flood level (Fig. 7). Across the slight topographic gradient found in the modern terrace at our site, we determined the numbers of transects and soil samples to be collected across using an a priori test of statistical power, which anticipated two main effects: soil type and soil depth, assuming a moderate statistical power of 0.8 for each effect68. Thirty maximum contrast profiles were sampled with a Dutch auger every 10 cm up to 1 m depth to a total of 300 samples of ~200 g each. Uncompressed soil cores were obtained continuously at each profile using metal rings to determine the bulk density at each depth. Coarse litter was removed from the topsoil before sampling. Prior to analysis all samples were allowed to air-dry for 2 weeks under the shade, sieved to <2 mm, sterilized, and finely ground in an agate ball mill.

### Organic carbon analysis

Total soil organic carbon was determined through combustion and gas chromatography in a standard elemental analyser (Costech, USA). For pyrogenic carbon determination, the fine soil fraction was dried and homogenised. Aliquots from each sample were ground in a ball mill and digested using acid-peroxide69. Ground aliquots (1 g) were placed in Erlenmeyer flasks (50 ml) to which 30% H2O2 (20 ml) and 1 M HNO3 (10 ml) were added and swirled by hand at room temperature for 30 minutes. Flasks were heated in a water bath to 90 °C for 16 hours. After digestion, the samples were filtered through pre-weighed Whatman glass filters (1.21 μm), which were dried at 60 °C for over 24 hours and weighed to obtain the mass of residual material after filtration. Aliquots were oven-dried and the mass of the residue (digested sample) was determined by weight difference. Microcharcoal particles (<150 μm) comprise most of the charcoal pool at our site and very small particles (<40 μm) dominate pretic ADE horizons5. Accordingly, the results obtained here using digestions of the whole fine soil fraction, is considered to be representative of the whole microcharcoal pool. The estimated amount of microcharcoal can be calculated for each soil type assuming that all non-charcoal organics were fully consumed during peroxide-acid digestion:

$$PyC = \left( \frac {C_1 * M_1}{M_2} \right),$$
(1)

where PyC is the mass of pyrogenic carbon; C1 is the carbon concentration in the digested sample; M1 is the mass of the digested sample, and M2 is the mass of the original soil sample.

Soil carbon age-depth models were developed using calibrated radiocarbon (14C) activity of bulk soil organic matter and pyrogenic carbon from multiple depths in ADE and Ultisol profiles. Radiocarbon dating and calibration of 14C ages to years before present were performed at the University of California Irvine, through accelerator mass spectrometry. Samples were collected in soil pits dug adjacent to each transect to determine the age of 15 samples (8 bulk soil organic carbon samples and 7 PyC samples) collected from ADE and Ultisol horizons, as described above. Bulk carbon samples were analysed after drying and sieving. A modern charcoal standard was created by combusting dry modern wood tissue from plants growing near the study. All pyrogenic carbon samples, including the modern standard and an old charcoal standard with no detectable radiocarbon activity (for contamination control purposes), were cleaned using alternating heated 10% KOH and 10% HCL rinses prior to analysis. Human activity and natural disturbance may have contributed additional charcoal into the soil matrix, and thus the calibrated 14C dates reported here represent the most recent of a range of possible ages of carbon input.

### Elemental analysis

Extractable P and Ca were determined using atomic absorption spectrophotometry. Mehlich 1 (0.025 N H2SO4 + 0.05 N HCl) was used for P extractions and KCl (1 N) was used for Ca extractions. For total nutrient concentrations, ~200 mg of finely ground soil was digested in PFA vessels on a Teflon-coated graphite block digestor (Model A3, Analysco Ltd, Chipping Norton, UK). Acid digestion was initially with 2 ml of HNO3 (68% Primar Plus grade) and 1 ml of HClO4 heated at 80 °C for 8 h and subsequently at 100 °C for 2 h. The following day 2.5 ml of HF (40% AR) was added to the tubes and the temperature raised to 120 °C for 1 h, increased and maintained at 140 °C for 3 h, then 160 °C for 4 h; the vessels were again left overnight at room temperature. On the third day, the block digester was set to 50 °C and 2.5 ml of HNO3 and 2.5 ml Milli-Q water (18.2 MΩ cm; Fisher Scientific UK Ltd, Loughborough, UK) were added to tubes and left at 50 °C for one hour. After cooling, the digested samples were washed with Milli-Q water into 50 ml plastic flasks and stored in a 5% HNO3 matrix at room temperature in universal sample bottles pending elemental analysis. The standard reference material (SRM 2711a Montana soil, National Institute of Standards and Technology-NIST, Gaithersburg, MD, USA) and blank digests were included with every batch of 48 samples. Subsequent analysis of Ag, Al, As, Ba, Be, Ca, Cd, Co, Cu, Cr, Cs, Fe, K, Li, Mg, Mn, Mo, Ni, P, Pb, Rb, Se, Sr, Ti, Tl, U, V and Zn was carried out by inductively coupled plasma mass spectrometry (ICP-MS; Model iCAP-Q™, ThermoScientific, Bremen, Germany). All samples were blank-corrected using the operational digestion blanks6.

### Isotopic analysis

Samples from the surface and deep soil layers were used to determine stable isotope ratios of carbon, strontium, and neodymium. For carbon isotope ratios (δ13C), bulk organic carbon was determined by dry combustion gas chromatography coupled with continuous‐flow isotopic‐ratio mass spectrometry (GC-IRMS; Europa, Crewe, UK) at the University of California, Davis. To calculate the contribution of forest and savannas at different points in time, the 14C age-depth model was combined with typical δ13C signatures of C3 trees (−25.9‰ ± 0.4) and C4 grasses (−11.2‰ ± 0.2) in the study region43 in a two‐end member mixing model70:

$$C_4 = C_t(\delta _t - \delta _3)/(\delta _4 - \delta _3),$$
(2)

where $$C_t$$ is the total mass of organic carbon in the soil coming from C3 and C4 sources; C3 is the mass of carbon derived from trees and herbaceous plants that assimilate carbon through the C3 metabolic pathway; C4 is the amount of carbon derived from grasses which assimilate carbon through the C4 metabolic pathway; δt is the δ13C ratio of Ct; δ3 is the δ13C ratio of C3-derived organic carbon, and δ4 is the δ13C ratio of grass-derived organic carbon expressed as the relative (percentage) of grass input to the total organic carbon pool.

The isotopic ratios of soil carbon incorporate changes in atmospheric CO2 due to the emission of fossil fuels over the past century. However, changes in δ13C ratios of CO2 have been small for most of the Holocene (<1.5‰ over the past 10,000 years71) and affected both tree and grass signatures. We can therefore rule out this effect as an explanation for long-term changes in carbon source observed here. After organic matter deposition, diagenetic fractionation occurs primarily in the topsoil as a function of decomposition, typically leading to a <2‰ fractionation72, a result that can be observed here within the top 20 cm of ADE and Ultisol profiles (Fig. 4). Other sources of variation, such as changes in plant water-use efficiency in response to atmospheric CO2, are not relevant at the scale studied here because this effect would be smaller than differences between δ3 and δ4. We can also rule out any confounding effect of inorganic carbon, which were absent from our samples, as expected due to moderate acidity (pH 5.11–5.73) of ADEs and extreme acidity of Ultisols at our site (pH 4.12)5.

For the analysis of Sr and Nd isotopes, soil samples were digested in two stages using concentrated HF/HNO3 and 6 N HCl in Teflon Savillex beakers placed on a hot plate. In order to determine the 87Sr/86Sr ratio, another aliquot of the initial solution was submitted to chromatography over SR-B50-A resin (Eichrom, Lisle, IL, USA; particle size 100e150 m) using 2.9 M HNO3 as eluent. The determination of 87Sr/86Sr ratios was performed using a ThermoFisher Triton, involving 30 cycles in one block. During the course of sample measurements, repeated determination of Sr isotopes in a 100 ppm solution of NIST SRM 987 strontium carbonate (87Sr/86Sr = 0.71036 ± 0.00026), yielded an average value of 0.71025 ± 0.00008, n = 12. An aliquot of this solution was used for mineral extractions adapted specifically for Amazonian Oxisols, in which trace elements were separated as a group using cation-exchange columns73. Following this procedure, a reversed-phase chromatography was applied for Samarium–neodymium (Sm–Nd) radiometric dating using columns loaded with HDEHP (di-2-ethylhexeyl phosphoric acid) supported on Teflon powder. A mixed 149Sm–150Nd spike was used with re-evaporation filaments of a double filament assembly. The isotopic analyses were performed using a ThermoFisher Triton multi-collector mass spectrometer in static mode. Uncertainties for Sm/Nd and 143Nd/144Nd ratios were ±0.1% (2σ) and 0.005% (2σ), respectively, based on repeated analyses of international rock standards BCR-1 and BHVO-1, normalised to a 146Nd/144Nd ratio of 0.7129 using blanks smaller than 100 pg. Considering that ADE is a mixture of weathered minerals found in typical Ultisols with exogenous inputs (Supplementary Fig. 3), the contribution of river sediment to the total pool found in the ADE was calculated using the mass of Sr and its stable isotope ratios (87Sr/86Sr) measured in the surrounding Ultisol and river water as follows:

$$Sr_{{\mathrm{ADE}}} = {{Sr}}_{{\mathrm{Ultisol}}}\left( {{\,}^{87}{{Sr}}/{\,}^{86}{{Sr}}} \right)_{{\mathrm{Ultisol}}} + {\mathrm{Sr}}_{{\mathrm{river}}}\left( {{\,}^{87}{{Sr}}/{\,}^{86}{{Sr}}} \right)_{{\mathrm{river}}}.$$
(3)

#### Population density estimates

The first step we used to estimate the size of human populations and the amount of inputs needed to create the studied ADE was to calculate how much additional mass of human inputs would be needed to explain excess Ca and P in the ADE relative to the stocks in the surrounding Ultisol (for a total soil depth of 1 m; Fig. 3). By focusing on Ca and P stocks we implicitly represent the depositional history of 16 other mineral elements which correlate significantly with P and Ca at the site (Supplementary Fig. 1). The second step to calculate human inputs was to consider the possible anthropic sources of Ca and P under the assumption that population densities are directly related to the amount of waste deposited onto soils. To minimise uncertainties related to type of biomass deposited we considered three sources that are often attributed to ADE genesis: human faeces, plant biomass, and fish biomass. Fish waste is the richest of those sources, and thus, it yields the most conservative population densities. The third step was to consider the time needed to generate the observed excess fertility in the ADE via the consumption of fish by a certain number of people:

$$Q = D_t \, 0.2M_t/TP,$$
(4)

where Q is protein available from fish per capita per day in grams; Dt is the number of person-days fishing for period T in days; Mt is the dressed weight in grams of the average day’s catch of one for the period, and P is the average population subsisting on the protein obtained over T. The constant (0.2) is a rough value indicating the protein yield from any given quantity of fresh, dressed meat or fish obtained by inspecting the values for protein in 100 g edible portions of several kinds of meat and fish in indigenous communities of Latin America58.

### Reporting summary

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

## Data availability

The data used to produce all figures and supplementary materials present here are available at https://doi.org/10.7264/9qdm-en61

## References

1. 1.

Sombroek, W. G. Amazon Soils. A Reconnaissance of the Soils of the Brazilian Amazon Region 292 (Wageningen, Netherlands, 1966).

2. 2.

Palace, M. W. et al. Ancient Amazonian populations left lasting impacts on forest structure. Ecosphere 8, e02035 (2017).

3. 3.

Lehmann, J. Amazonian Dark Earths: Origin Properties Management (Kluwer Academic Publishers, Netherlands, 2003).

4. 4.

Glaser, B. & Birk, J. J. State of the scientific knowledge on properties and genesis of Anthropogenic Dark Earths in Central Amazonia (terra preta de Índio). Geochim. Cosmochim. Acta 82, 39–51 (2012).

5. 5.

Macedo, R. S., Teixeira, W. G., Corrêa, M. M., Martins, G. C. & Vidal-Torrado, P. Pedogenetic processes in anthrosols with pretic horizon (Amazonian Dark Earth) in Central Amazon, Brazil. PLoS ONE 12, e0178038 (2017).

6. 6.

Barbosa, J. Z. et al. Elemental signatures of an Amazonian Dark Earth as result of its formation process. Geoderma 361, 114085 (2020).

7. 7.

Quesada, C. A. et al. Variations in soil chemical and physical properties explain basin-wide Amazon forest soil carbon concentrations. Soil 6, 53–88 (2020).

8. 8.

Grau, O. et al. Nutrient-cycling mechanisms other than the direct absorption from soil may control forest structure and dynamics in poor Amazonian soils. Sci. Rep. 7, 45017 (2017).

9. 9.

Silva, L. C. R. & Lambers, H. Soil-plant-atmosphere interactions: structure, function, and predictive scaling for climate change mitigation. Plant Soil 1–23 https://doi.org/10.1007/s11104-020-04427-1 (2020).

10. 10.

Haridasan, M. Nutritional adaptations of native plants of the cerrado biome in acid soils. Braz. J. Plant Physiol. 20, 183–195 (2008).

11. 11.

Morello, T. F. et al. Fertilizer adoption by smallholders in the Brazilian Amazon: Farm-level evidence. Ecol. Econ. 144, 278–291 (2018).

12. 12.

Lombardo, U. et al. Early Holocene crop cultivation and landscape modification in Amazonia. Nature 581, 190–193 (2020).

13. 13.

Capriles, J. M. et al. Persistent early to middle Holocene tropical foraging in southwestern Amazonia. Sci. Adv. 5, eaav5449 (2019).

14. 14.

Bush, M. B. et al. A 6900-year history of landscape modification by humans in lowland Amazonia. Quat. Sci. Rev. 141, 52–64 (2016).

15. 15.

Maezumi, S. Y. et al. The legacy of 4,500 years of polyculture agroforestry in the eastern Amazon. Nat. Plants 4, 540–547 (2018).

16. 16.

Kern, D. C. et al. Terras pretas: approaches to formation processes in a new paradigm. Geoarchaeology 32, 694–706 (2017).

17. 17.

McMichael, C. H. et al. Predicting pre-Columbian anthropogenic soils in Amazonia. Proc. R. Soc. B Biol. Sci. 281, 20132475 (2014).

18. 18.

Schmidt, M. J. et al. Dark earths and the human built landscape in Amazonia: a widespread pattern of anthrosol formation. J. Archaeol. Sci. 42, 152–165 (2014).

19. 19.

Birk, J. J., Teixeira, W. G., Neves, E. G. & Glaser, B. Faeces deposition on Amazonian Anthrosols as assessed from 5β-stanols. J. Archaeol. Sci. 38, 1209–1220 (2011).

20. 20.

Glaser, B. Prehistorically modified soils of central Amazonia: a model for sustainable agriculture in the twenty-first century. Philos. Trans. R. Soc. Lond. B Biol. Sci. 362, 187–196 (2007).

21. 21.

El-Naggar, A. et al. Biochar application to low fertility soils: a review of current status, and future prospects. Geoderma 337, 536–554 (2019).

22. 22.

Cunha, T. J. F. et al. Soil organic matter and fertility of anthropogenic dark earths (Terra Preta de Índio) in the Brazilian Amazon basin. Rev. Bras. Cienc. do Solo 33, 85–93 (2009).

23. 23.

Lutfalla, S. et al. Pyrogenic carbon lacks long-term persistence in temperate arable soils. Front. Earth Sci. 5, 96 (2017).

24. 24.

Chadwick, K. D. & Asner, G. P. Landscape evolution and nutrient rejuvenation reflected in Amazon forest canopy chemistry. Ecol. Lett. 21, 978–988 (2018).

25. 25.

Chadwick, O. A., Derry, L. A., Vitousek, P. M., Huebert, B. J. & Hedin, L. O. Changing sources of nutrients during four million years of ecosystem development. Nature 397, 491–497 (1999).

26. 26.

Vitousek, P. M. Nutrient Cycling and Limitation: Hawai’i as a Model System. Ecology Vol. 30 (Princeton University Press, 2004).

27. 27.

Silva, L. C. R. et al. Can savannas become forests? A coupled analysis of nutrient stocks and fire thresholds in central Brazil. Plant Soil 373, 829–842 (2013).

28. 28.

Alho, C. F. B. V. et al. Spatial variation of carbon and nutrients stocks in Amazonian Dark Earth. Geoderma 337, 322–332 (2019).

29. 29.

Bomfim, B., Silva, L. C. R., Doane, T. A. & Horwath, W. R. Interactive effects of land-use change and topography on asymbiotic nitrogen fixation in the Brazilian Atlantic Forest. Biogeochemistry 142, 137–153 (2019).

30. 30.

Hendrixson, H. A., Sterner, R. W. & Kay, A. D. Elemental stoichiometry of freshwater fishes in relation to phylogeny, allometry and ecology. J. Fish. Biol. 70, 121–140 (2007).

31. 31.

Nishimuta, M. et al. Moisture and mineral content of human feces–high fecal moisture is associated with increased sodium and decreased potassium content. J. Nutr. Sci. Vitaminol. 52, 121–126 (2006).

32. 32.

Rossetti, D. F. et al. Unfolding long-term late Pleistocene-Holocene disturbances of forest communities in the southwestern Amazonian lowlands. Ecosphere 9, e02457 (2018).

33. 33.

Carson, J. F. et al. Pre-Columbian land use in the ring-ditch region of the Bolivian Amazon. Holocene 25, 1285–1300 (2015).

34. 34.

Shepard, G. H. et al. in Oxford Research Encyclopedia of Environmental Science (Hazlitt, R. ed.) (Oxford, 2020).

35. 35.

Arroyo-Kalin, M. Slash-burn-and-churn: Landscape history and crop cultivation in pre-Columbian Amazonia. Quat. Int. 249, 4–18 (2012).

36. 36.

Brugger, S. O. et al. Long-term man-environment interactions in the Bolivian Amazon: 8000 years of vegetation dynamics. Quat. Sci. Rev. 132, 114–128 (2016).

37. 37.

Maezumi, S. Y. et al. New insights from pre-Columbian land use and fire management in Amazonian dark earth forests. Front. Ecol. Evol. 6, 111 (2018).

38. 38.

Zani, H., Rossetti, D. F., Cohen, M. L. C., Pessenda, L. C. R. & Cremon, E. H. Influence of landscape evolution on the distribution of floristic patterns in northern Amazonia revealed by δ13C data. J. Quat. Sci. 27, 854–864 (2012).

39. 39.

Lombardo, U. et al. Holocene land cover change in south-western Amazonia inferred from paleoflood archives. Glob. Planet. Change 174, 105–114 (2019).

40. 40.

Ward, B. M. et al. Reconstruction of Holocene coupling between the South America Monsoon System and local moisture variability from speleothem δ18O and 87Sr/86Sr records. Quat. Sci. Rev. 210, 51–63 (2019).

41. 41.

Wortham, B. E. et al. Assessing response of local moisture conditions in central Brazil to variability in regional monsoon intensity using speleothem 87Sr/ 86Sr values. Earth Planet. Sci. Lett. 463, 310–322 (2017).

42. 42.

Silva, L. C. R. Importance of climate-driven forest–savanna biome shifts in anthropological and ecological research. Proc. Natl Acad. Sci. USA 111, E3831–E3832 (2014).

43. 43.

Wright, J. et al. Sixteen hundred years of increasing tree cover prior to modern deforestation in Southern Amazon and Central Brazilian savannas. Glob. Chang. Biol. https://doi.org/10.1111/gcb.15382 (2020).

44. 44.

Bomfim, B. et al. Fire affects asymbiotic nitrogen fixation in Southern Amazon Forests. J. Geophys. Res. Biogeosci. 125, (2020).

45. 45.

Rossetti, D. F., Bertani, T. C., Zani, H., Cremon, E. H. & Hayakawa, E. H. Late Quaternary sedimentary dynamics in Western Amazonia: Implications for the origin of open vegetation/forest contrasts. Geomorphology 177–178, 74–92 (2012).

46. 46.

Hoffmann, W. A. et al. Ecological thresholds at the savanna-forest boundary: How plant traits, resources and fire govern the distribution of tropical biomes. Ecol. Lett. 15, 759–768 (2012).

47. 47.

Roddaz, M. et al. Evidence for the control of the geochemistry of Amazonian floodplain sediments by stratification of suspended sediments in the Amazon. Chem. Geol. 387, 101–110 (2014).

48. 48.

Santos, R. V. et al. Source area and seasonal 87Sr/86Sr variations in rivers of the Amazon basin. Hydrol. Process. 29, 187–197 (2015).

49. 49.

Passos, M. S. et al. Pleistocene-Holocene sedimentary deposits of the Solimões-Amazonas fluvial system, Western Amazonia. J. South Am. Earth Sci. 98, 102455 (2020).

50. 50.

Bayon, G. et al. Rare earth elements and neodymium isotopes in world river sediments revisited. Geochim. Cosmochim. Acta 170, 17–38 (2015).

51. 51.

Quintana-Cobo, I. et al. Dynamics of floodplain lakes in the Upper Amazon Basin during the late Holocene. Comptes Rendus Geosci. 350, 55–64 (2018).

52. 52.

Hayakawa, E. H., Rossetti, D. F., Hayakawa, E. H. & Rossetti, D. F. Late quaternary dynamics in the Madeira river basin, southern Amazonia (Brazil), as revealed by paleomorphological analysis. Acad. Bras. Cienc. 87, 29–49 (2015).

53. 53.

Gonçalves, E. S., Soares, E. A. A., Tatumi, S. H., Yee, M. & Mittani, J. C. R. Pleistocene-Holocene sedimentation of Solimões-Amazon fluvial system between the tributaries Negro and Madeira, Central Amazon. Braz. J. Geol. 46, 167–180 (2016).

54. 54.

Viers, J. et al. Seasonal and provenance controls on Nd–Sr isotopic compositions of Amazon rivers suspended sediments and implications for Nd and Sr fluxes exported to the Atlantic Ocean. Earth Planet. Sci. Lett. 274, 511–523 (2008).

55. 55.

Sant’Anna, L. G. et al. Age of depositional and weathering events in Central Amazonia. Quat. Sci. Rev. 170, 82–97 (2017).

56. 56.

Guyot, J. L. et al. Clay mineral composition of river sediments in the Amazon Basin. CATENA 71, 340–356 (2007).

57. 57.

Macedo, R. S. et al. Amazonian dark earths in the fertile floodplains of the Amazon River, Brazil: An example of non-intentional formation of anthropic soils in the Central Amazon region. Bol. do Mus. Para. Emilio Goeldi Cienc. Humanas 14, 207–227 (2019).

58. 58.

Gross, D. R. Protein capture and cultural development in the Amazon basin. Am. Anthropol. 77, 526–549 (1975).

59. 59.

Bomfim, B. et al. Litter and soil biogeochemical parameters as indicators of sustainable logging in Central Amazonia. Sci. Total Environ. 714, 136780 (2020).

60. 60.

Lehmann, J. et al. Nutrient availability and leaching in an archaeological Anthrosol and a Ferralsol of the Central Amazon basin: fertilizer, manure and charcoal amendments. Plant Soil 249, 343–357 (2003).

61. 61.

Gay‐des‐Combes, J. M. et al. Tropical soils degraded by slash‐and‐burn cultivation can be recultivated when amended with ashes and compost. Ecol. Evol. 7, 5378–5388 (2017).

62. 62.

Isendahl, C. & Smith, M. E. Sustainable agrarian urbanism: The low-density cities of the Mayas and Aztecs. Cities 31, 132–143 (2013).

63. 63.

Clement, C. R. et al. The domestication of Amazonia before European conquest. Proc. R. Soc. B Biol. Sci. 282, 20150813 (2015).

64. 64.

de Souza, J. G. et al. Climate change and cultural resilience in late pre-Columbian Amazonia. Nat. Ecol. Evol. 3, 1007–1017 (2019).

65. 65.

Mongeló, G. Early and Middle Holocene human occupations in Southwest Amazon. Bol. Mus. Para. Emílio Goeldi. Cienc. Hum. https://doi.org/10.1590/2178-2547-bgoeldi-2019-0079 (2020).

66. 66.

Kistler, L. et al. Multiproxy evidence highlights a complex evolutionary legacy of maize in South America. Science 362, 1309–1313 (2018).

67. 67.

Denevan, W. M. A Bluff model of riverine settlement in prehistoric Amazonia. Ann. Assoc. Am. Geogr. 86, 654–681 (1996).

68. 68.

Silva, L. C. R., Corrêa, R. S., Doane, T. A., Pereira, E. I. P. & Horwath, W. R. Unprecedented carbon accumulation in mined soils: the synergistic effect of resource input and plant species invasion. Ecol. Appl. 23, 1345–1356 (2000).

69. 69.

Kurth, V. J., MacKenzie, M. D. & DeLuca, T. H. Estimating charcoal content in forest mineral soils. Geoderma 137, 135–139 (2006).

70. 70.

Silva, L. C. R. et al. Iron-mediated stabilization of soil carbon amplifies the benefits of ecological restoration in degraded lands. Ecol. Appl. 25, 1226–1234 (2015).

71. 71.

Hare, V. J., Loftus, E., Jeffrey, A. & Ramsey, C. B. Atmospheric CO2 effect on stable carbon isotope composition of terrestrial fossil archives. Nat. Commun. 9, 252 (2018).

72. 72.

Krull, E. S., Bestland, E. A. & Gates, W. P. Soil organic matter decomposition and turnover in a tropical Ultisol: evidence from δ13C, δ15N and geochemistry. Radiocarbon 44, 93–112 (2002).

73. 73.

Gioia, S. M. C. L. & Pimentel, M. M. The Sm-Nd isotopic method in the Geochronology Laboratory of the University of Brasília. Acad. Bras. Cienc. 72, 218–245 (2000).

## Acknowledgements

We thank the National Science Foundation (AGS#1602958; Convergence Accelerator #1939511), the Brazilian Council for Scientific and Technological Development – CNPq, and the 2019 Resilience Initiative Interdisciplinary Award at the University of Oregon for research funding. All samples were collected, processed, and analysed in coordination with the local authorities and following Brazilian laws and regulations. We thank Dr William Horwath for logistical support in the USA and Dr Wenceslau Geraldes Teixeira for providing logistical support in Brazil and for hosting international training events including field courses at EMBRAPA CPAA, which catalysed this collaboration. The publication fees for this article were supported by the University of Oregon Libraries Open Access Article Processing Charge Fund.

## Author information

Authors

### Contributions

L.C.R.S.: Designed the study, generated and analysed data, made figures and wrote the manuscript. R.S.C.: Designed the study, collected samples, interpreted elemental data, and revised manuscript. J.L.W.: Integrated data sets and performed spatial analysis. B.B.: Analysed charcoal samples and interpret biogeochemical data. L.H.: Digested samples and quantified pyrogenic carbon. D.G.: Generated elevation maps, oversaw pyrogenic carbon analysis, and revised manuscript. A.W.M.: Collected soil samples, provided resources, and preliminary data. G.C.M.: Collected soil samples and generated preliminary data. A.C.V.M.: Performed laboratory work and helped with data analysis. J.Z.M.: Organised data and helped interpret elemental inputs. V.d.F.M.: Helped with the analysis and interpretation of elemental data. S.D.Y.: Provided resources and oversaw chemical analysis. M.R.B.: Provided resources, helped with multi-proxy data interpretation, and revised manuscript. R.V.S.: Generated isotopic data, interpreted geological sources, and revised manuscript.

### Corresponding author

Correspondence to Lucas C. R. Silva.

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Silva, L.C.R., Corrêa, R.S., Wright, J.L. et al. A new hypothesis for the origin of Amazonian Dark Earths. Nat Commun 12, 127 (2021). https://doi.org/10.1038/s41467-020-20184-2

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